Binding of 1,1,1-trichloro-2,2-di-p-chlorophenylethane (DDT) with subcellular fractions of rat brain

DDT (1,1,1-trichloro-2,2-di-p-chlorophenylethane) and DDE (1,1-dichloro-2,2-di-p-chlorophenylethylene, a non-insecticidal analogue of DDT) were found to bind with various nerve components of rat brain. The amount of DDT binding exceeded that of DDE only in the fraction containing mainly the nerve endings. Among various components in the nerve-ending fraction, a subfraction containing mainly the pre- and post-synaptic complexes had the highest affinity for DDT in comparison with that for DDE. By using an ;acetone-powdering' technique on brain preparations, the Sephadex-column method was shown to provide reliable results for studies on the binding of DDT or DDE with soluble proteins in the nerve tissues. From these results it was concluded that DDE had a higher affinity for soluble components of the rat brain than did DDT.     

Elevated Concentrations of Pesticides and PCBs in Soils at the Southern Caspian Sea (Iran) are Related to Land Use

Soil contamination by organochlorine pesticides or PCBs is almost undocumented for Iran. Here we report a soil survey in Mazandaran and Guilan provinces that hold >30% of the agricultural areas of Iran where pesticide use is widespread. Concentration of DDTs, HCHs, cyclodienes, and PCBs were measured in 45 soil samples from different agricultural land uses and forest land. The average concentrations of ∑DDT (37 μg kg^?1) and ∑HCH (21 μg kg^?1) in agricultural soils are among the largest ever reported and exceed international soil screening standards. All residues were larger in agricultural than in forest soil. Within agricultural land, ∑DDT were largest for tea gardens, lindane was largest in rice fields, and cyclodiens largest in citrus orchards. The ratio of (DDD + DDE)/DDT is an index of the extent of DDT degradation in soil and was lower in tea gardens than in other soils (0.7 versus 2–5), indicating either ongoing DDT input or lower degradation rate in the tea gardens that are more acid than the other soils (pH 4.5 versus 6.5–7.0). The o,p′–DDT/p,p′–DDT ratio was about 3 in forest soils, suggesting that DDT is derived from dicofol application and not from technical DDT as in agricultural soils. The PCB 28, 180, and 138 showed the highest mean concentration compared with other PCB congeners in all land uses. This survey is the first of this kind for Iran and illustrates that concentrations of organochlorine pesticide in soil are relatively large.     

Thyroid hormone-dependent gene expression as a biomarker of short-term 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene (DDE) exposure in European common frog (Rana temporaria) tadpoles

The effects on thyroid hormone-dependent gene biomarker responses of the persistent organochlorine pesticide metabolite 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene (DDE) were investigated after exposure of 4-week-old European common frog (Rana temporaria) (stage 36) tadpoles to two (0.001 and 0.01 ppm) DDE concentrations. Total body weight, total length, and tail length and width increased after 3-day exposure to DDE. Expression patterns of genes encoding for growth hormone, thyroid-stimulating hormone (TSHβ) and thyroid hormone receptor (TRα and TRβ) isoforms were evaluated in the head, body and tail regions using a validated real-time polymerase chain reaction (PCR) method. The mRNA expression of growth hormone in the body, and TSHβ in the head showed significant DDE concentration-dependent decreases. While DDE caused variable effects on TRα mRNA steady-state, the expression of TRβ was significantly decreased in the tail by DDE in a concentration-specific manner. The effect of DDE exposure on TRβ mRNA expression showed a negative correlation with tail length and width during the exposure period. The unique pattern of a DDE-induced decrease of tail TRβ expression probably reflects the significant role of this thyroid hormone receptor isoform in tail re-absorption and overall metamorphosis in anuran species. Therefore, the present study shows that the evaluation of thyroid hormone-dependent genes may represent quantitative biomarkers of acute exposure to organochlorine pesticides in anuran species during critical developmental periods such as metamorphosis. Given the widespread environmental levels of DDT and its metabolites, these pollutants will remain a subject of concern and their effects on anuran species should be studied in more detail.     

Modification of ion transport in lipid bilayer membranes by the insecticides DDT and DDE

In order to elucidate the mechanism of action of organochlorine insecticides on the ion transport in biological membranes, we have studied the effect of DDT and its analog DDE on the structural parameters of phosphatidylethanolamine (PE) planar bilayers. DDT and DDE increase the conductance induced by the hydrophobic ions tetraphenylarsonium (TPhAs⁺) and tetraphenylborate (TPhB^?) in lipid bilayers. Neither DDT nor DDE alters the surface potential of PE monolayers. On the other hand, these organochlorine compounds increase only slightly the electric capacitance of the bilayers. These results are compatible with the hypothesis that these insecticides increase the fluidity of the membrane.     

Effects of PCBs, DDT, and mercury compounds in chickens and Japanese quail.

In well-controlled experiments using white leghorn chickens and Japanese quail, dietary polychlorinated biphenyls (PCBs), DDT and related compounds produced no detrimental effects on eggshell quality. A drastic reduction in hatchability of chicks occurred with 10-20 ppm PCBs, but no detrimental effects on eggshell quality, egg production or hatchability were found with 0.5 and 1.0 ppm PCBs, or DDT up to 100 ppm. Dietary PCBs potentiated a vitamin E-selenium deficiency in the chick, increased exudative diathesis, and decreased plasma glutathione peroxidase levels. Dietary PCBs induced hepatic microsomal benzopyrine hydroxylase. Dietary levles of 100 or 200 ppm inorganic mercury as HgSO4 or HgCl2 had little effect on egg production, hatchability, shell quality, morbidity and mortality. Methylmercury chloride, however, at levels providing 10 or 20 mg Hg/kg of diet, severely affected all of these parameters. Even though the present experiments demonstrate that neither DDT nor PCBs has any effect on eggshell quality in chickens and Japanese quail, they may cause thinning of eggshells in other species. Controlled experiments are lacking. Eagles, ospreys and pelicans all consume fish which in many areas of the world are known to contain methyl mercury. The thinning of eggshells in the species in the wild may have been due, at least in part, to environmental contamination with methylmercury rather than DDT, DDE or PCBs, as has been claimed.     

Inheritance of DDT dehydrochlorination and of a mechanism restricting uptake of DDT in the mosquito Aedes aegypti

Crosses and backcrosses were made between the T8 dichlorodiphenyltrichloroethane (DDT) resistant strain and NS susceptible strain. Each generation was tested for resistance, for internal levels of DDT and dichlorodiphenyldichloroethylene (DDE) (thus "DDT uptake" (DDT + DDE) and percentage DDT dehydrochlorination in vivo), and for DDT dehydrochlorination in vitro, both at the larval and adult stages. The patterns of inheritance of uptake and dehydrochlorination were different. At both life stages, dehydrochlorination (both in vivo and in vitro) was intermediate in the F1, reverting to or exceeding the parental strains in the backcrosses except in adult tests on the backcrosses to the susceptible strain where it remained intermediate. Uptake increased very substantially in the F1 compared with either parental strain and was also high in the backcrosses. This was interpreted as being due to the disruption of an uptake-restricting mechanism in T8 brought about by outcrossing. Larval resistance in the various generations was correlated significantly with dehydrochlorination, both in vivo and in vitro but bore no clear relation to uptake. Resistance in adults was found not to be correlated significantly with either.     

Causes of resistance to DDT in a diazinon-selected and a DDT-selected strain of house flies

The causes of resistance to DDT in a DDT-selected (F58W) and a diazinon-selected (SKA) strain of house flies differed.Small (1 g DDT/fly) topically applied doses penetrated more slowly into the SKA than into the F58W or susceptible strains. Large doses (32 g/fly) penetrated equally fast into all strains.The two resistant strains metabolised DDT rapidly and the susceptible strain slowly. The only metabolite identified was DDE.WARF anti-resistant is a powerful synergist for DDT in the F58W strain, and prevents the formation of DDE. WARF anti-resistant is not such a good synergist in the SKA strain which possesses other mechanisms for metabolising DDT and also DDE.DDT or its decomposition products seem to interact strongly with the tissues of SKA flies from which they are not readily extracted.

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Zusammenfassung Gaschromatographie und radioaktive Markierungsverfahren wurden in Verbindung mit Papier- und Dünnschichtchromatographie benutzt, um die Urschen der Resistenz gegenüber DDT in einem mit DDT selektierten (F58W) und einem mit Diazinon selektierten Stamm (SKA) der Stubenfliege aufzuklären.DDT drang unterschiedlich in die zwei resistenten Stämme ein, die beide DDT rasch abbauten, sich aber in den Entgiftungsmechanismen unterschieden.Kleine Dosen (1 g DDT pro Fliege), die äußerlich aufgebracht wurden,töteten den empfindlichen Stamm, aber nicht den F58W- oder den SKA-Stamm, DDT drang in den SKA-Stamm langsamer ein als in die beiden anderen Stämme. Der eindringende DDT-Anteil nahm in den drei Stämmen unterschiedlich ab, wenn die Dosis anstieg, und bei hohen Dosen (32 g pro Fliege) vollzog sich das Eindringen in alle drei Stämme ungefähr gleich schnell.Das DDT wurde in den beiden resistenten Stämmen schnell, in dem anfälligen langsam abgebaut. Das einzige Abbauprodukt, das in den drei Stämmen identifiziert wurde, war DDE. In F58W und dem empfindlichen Stamm wurde die Masse des abgebauten DDT als DDE gefaßt.Die Bildung von DDE aus DDT wird in dem Stamm F58W durch das Antiresistent WARF verhindert, das die Toxizität des DDT erheblich steigert, wodurch sich zeigt, daß in diesem Stamm die Dehydrochlorierung eine wichtige Resistenzursache darstellt.In dem SKA-Stamm, der DDE abbaut, wurden nur Spuren von DDE gefunden. Jedoch stellt die Dehydrochlorierung in dem SKA-Stamm keine wesentliche Resistenzursache wie im F58W-Stamm dar, da WARF-Antiresistent kein starker DDT-Synergist ist. In dem SKA-F58W-Stamm wurde viel weniger von dem zugefügten DDT wiedergefunden als in den anderen Stämmen, wahrscheinlich weil DDT oder seine Abbauprodukte stärker mit den Geweben der SKA-Fliegen reagieren.

     

Pesticide-induced changes in hepatic microsomal enzyme systems. Some effects of 1,1-di(p-chlorophenyl)-2,2-dichloroethylene (DDE) and 1,1-di(p-chlorophenyl)-2-chloroethylene (DDMU) in the rat and Japanese quail

Hepatic microsomal protein, cytochrome P₄₅₀, aniline hydroxylase and N-ethylmorphine demethylase as well as tissue residues were measured following the feeding of low levels of 1,1-di(p-chlorophenyl)-2,2-dichloroethylene (DDE) or 1,1-di(p-chlorophenyl)-2-chloroethylene (DDMU) to rats and Japanese quail. DDMU caused considerable elevation of the levels of most of the parameters measured in the quail even by comparison to the potent inducer, DDE, which gave greater tissue residues. In the rat where tissue residues of both DDE and DDMU were lower than those in quail, DDE caused greater changes in the measured enzyme levels than DDMU. Most of the changes caused by DDMU in the quail were larger than those observed following the ingestion of comparable levels of any other 1,1-di(p-chlorophenyl)-2,2,2-trichloroethane (DDT) metabolite in the rat or the quail. In the light of these and other published results it is suggested that the metabolic pathway for DDT in birds differs from that in mammals and probably gives rise through a pathway involving DDMU to a highly active liver inducer.     

Thyroid hormone-dependent gene expression as a biomarker of short-term 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene (DDE) exposure in European common frog (Rana temporaria) tadpoles.

The effects on thyroid hormone-dependent gene biomarker responses of the persistent organochlorine pesticide metabolite 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene (DDE) were investigated after exposure of 4-week-old European common frog (Rana temporaria) (stage 36) tadpoles to two (0.001 and 0.01 ppm) DDE concentrations. Total body weight, total length, and tail length and width increased after 3-day exposure to DDE. Expression patterns of genes encoding for growth hormone, thyroid-stimulating hormone (TSHbeta) and thyroid hormone receptor (TRalpha and TRbeta) isoforms were evaluated in the head, body and tail regions using a validated real-time polymerase chain reaction (PCR) method. The mRNA expression of growth hormone in the body, and TSHbeta in the head showed significant DDE concentration-dependent decreases. While DDE caused variable effects on TRalpha mRNA steady-state, the expression of TRbeta was significantly decreased in the tail by DDE in a concentration-specific manner. The effect of DDE exposure on TRbeta mRNA expression showed a negative correlation with tail length and width during the exposure period. The unique pattern of a DDE-induced decrease of tail TRbeta expression probably reflects the significant role of this thyroid hormone receptor isoform in tail re-absorption and overall metamorphosis in anuran species. Therefore, the present study shows that the evaluation of thyroid hormone-dependent genes may represent quantitative biomarkers of acute exposure to organochlorine pesticides in anuran species during critical developmental periods such as metamorphosis. Given the widespread environmental levels of DDT and its metabolites, these pollutants will remain a subject of concern and their effects on anuran species should be studied in more detail.     

Effects of sex and sampling site on the relative proportion of pesticides in uropygial gland secretions of European Blackbirds (Turdus merula)

Dichlorodiphenyltrichloroethane (DDT) is a pesticide that was commonly used for decades worldwide. The use of DDT was banned in the 1970s and 1980s in Europe because of its high toxicity and persistence in the environment, bioaccumulation in living organisms and biomagnification through food webs. However, monitoring using both invasive and non-invasive methods has routinely reported the occurrence of DDT metabolites such as dichlorodiphenyldichloroethylene (DDE) in wild birds, providing valuable information about the exposure to pesticides and potential differences between species and over time. Here, we analysed the relative proportion of DDE in the uropygial gland secretions of European Blackbirds Turdus merula from two localities in southern Spain. Given the negative effects of this pollutant on animal immunity, we also tested for associations between the prevalence of haemosporidians and the relative proportion of DDE in their secretions. Relative proportions of DDE varied between sampling sites and were higher in females than in males, regardless of their age. In spite of the potential immunosuppressive effect of DDE, haemosporidian infection was not associated with DDE presence.     

Inhibition of the active transport of D-glucose and L-tyrosine by DDT and DDE in the rat small intestine

1. The effect of DDT and DDE on the active transport of D-glucose and L-tyrosine was studied in everted sacs of small intestine. 2. DDT and DDE (10(-5) and 10(-4) M) inhibit the active transport of D-glucose and L-tyrosine. 3. These organochlorine compounds also inhibit the (Na+ + K+)-ATPase from the same tissue, to about the same extent. 4. These results suggest that the inhibition of the active transport is due to an action of DDT and DDE on the sodium pump.     

Accumulation and degradation of organochorine pesticides in shellfish culture environment in Xiamen sea area

By using GC-ECD, the concentrations of organochlorine pesticides hexachlorocyclohexane (HCH) and dichlorodiphenyltrichloroethane (DDT) in the shellfish culture environment (sea water, sediments, and culture-shellfishes) in Xiamen sea area were analyzed, and the accumulation and degradation patterns of the HCH and DDT were preliminarily approached. In the sea area, there existed remarkable differences in the accumulation and degradation of HCH and DDT among different shellfish culture environments, being mostly associated with the habitation environment and physiological life habits of shellfish. The accumulated HCH isomers (Rx > 1) were mainly beta-HCH, delta-HCH, and gamma-HCH, whereas the degraded HCH isomers (Rx < 1) were mainly alpha-HCH. The ratio of alpha-HCH to gamma-HCH was less than or equal to 1.0, suggesting that the HCH was come from industrial HCH and lindane, most of the HCH had remained in the culture environment for a longer time, and a small amount of lindane was imported. The DDT in the sea water was aerobically degraded, its main degradation product was DDE, and the ratios of (DDD+DDE) to DDTs (p,p-DDE+p,p-DDD+o,p-DDT+p,p-DDT) was less than 0.5, whereas the DDT in sediments and shellfishes was anaerobically degraded, its main degradation product was DDD, and the ratios of (DDD+DDE) to DDTs was greater than 0.5, suggesting that there was a small amount of DDT newly imported in the sea water, and most DDT in sediments and shellfishes were already degraded and transformed into DDD and DDE. There were definite differences in the degradation rates of HCH isomers in the culture environment, suggesting the conformational change of HCH in its transformation processes in the shellfish culture ecosystem.     

Environmental pollutant and necropsy data for ospreys from the eastern United States, 1975-1982

Twenty-three ospreys (Pandion haliaetus) found dead or moribund in the eastern United States during 1975-1982 were necropsied and selected tissues were analyzed for organochlorines and metals. Major causes or factors contributing to death were trauma, impact injuries, and emaciation. DDE was detected in 96% of the osprey carcases, DDD in 65%, DDT and heptachlor epoxide in 13%, dieldrin, oxychlordane, and cis-nonachlor in 35%, cis-chlordane in 52%, trans-nonachlor in 45%, and PCB's in 83%. Carcasses of immature ospreys from the Chesapeake Bay had significantly lower concentrations of DDE, DDD + DDT, cis-chlordane, and PCB's than carcasses of adults from the same area. Concentrations of some organochlorines in ospreys from the Chesapeake Bay declined significantly from 1971-1973 to 1975-1982. Significant differences in concentrations of certain metals in the ospreys' livers were noted between time periods, and sex and age groups for birds from the Chesapeake Bay. During 1975-1982, adults had significantly lower concentrations of chromium, copper, and arsenic than immatures and nestlings, and adult males had higher mercury concentrations than adult females. Adult females had lower zinc concentrations in 1975-1982 than in 1971-1973. Immatures and nestlings had higher concentrations of chromium and lead in 1975-1982 than in 1971-1973. A slightly elevated concentration of chromium (1.7 ppm) or arsenic (3.2 ppm) was found in the livers of individual ospreys. Several ospreys had elevated concentrations of mercury in their livers; two ospreys had more than 20 ppm which may have contributed to their deaths.     

A Comparison of Ultrasonication and Soxhlet Methods for DDT Extraction from Soil

The goal of this study was to determine the efficacy of ultrasonication extraction of 1,1,1-trichloro-2,2-bis[p-chlorophenyl]ethane (DDT), 1,1-dichloro-2,2-bis[p-chlorophenyl]ethane (DDD), and 2,2-bis[p-chlorophenyl]1,1-dichloro-ethylene (DDE) residues in soil for the purposes of saving time, minimizing generation of hazardous solvent wastes, and reducing costs associated with monitoring contaminant concentrations at remediation sites. An ultrasonic extraction method was developed for DDT, DDD, and DDE residues in soil, and the efficiency of extraction using an ultrasonic cavitator was compared to the traditional soxhlet method by GC-MS. Un-contaminated soil was spiked with analytes DDT, DDD, and DDE at 0.1,1.0,10.0, and 100.0?mg/ kg. Experiments were performed in triplicate, and recoveries of analytes were determined and statistically compared. Results indicate that ultrasonic extraction is a suitable preparatory method for analysis of DDT, DDD, and DDE residues in soil. For spike concentrations of 1?mg/kg to 100?mg/kg, ultrasonication extraction resulted in recoveries in excess of 80% in all but one case. Most recoveries obtained by ultrasonication extraction were statistically indistinguishable from or slightly lower than recoveries obtained by soxhlet extraction. In addition, the lower temperatures employed in ultrasonication extraction may have reduced the amount of thermal degradation of DDT to DDE, a phenomenon that could occur during soxhlet extraction.     

Cytogenetic and mutagenic effects of DDT and DDE in a Chinese hamster cell line

The mutagenic and cytogenetic effects of the chlorinated hydrocarbon 1,11-trichloro-2,2-bis(p-chlorophenyl)ethane] (DDT), and its metabolite [1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene] (DDE) were investigated in vitro using a Chinese hamster cell line. A forward mutation system utilizing the 8-azaguanine sensitive to 8-azaguanine resistant marker was used as the index of mutagenic action. Methyl methanesulfonate (MMS) was used as the positive control. In all experiments, DDE consistently produced a significant increase in the mutation frequency over the control level, while DDT proved inactive.Resultsof the cytogenetic studies indicated that DDE-treated cells had a significant increase in chromosome aberrations over those occuring in the control population; exchange figures and chromatid breaks wre evident. DDT produced no significant increase in chromosome abnormalities. The Chinese hamster cell populations exposed to DDE also manifested an increased number of polyploid cells over the control level.     

Inhibition of photosynthetic electron transport by DDT and DDE

The effect of DDT and DDE (a metabolite of DDT) on chloroplast electron transport was investigated. Photosynthetic electron transport in isolated spinach and barley chloroplasts as well as chloroplasts isolated from macroscopic green algae,Cdium fragile andChaetomorpha aerea, was inhibited by both compounds. Photoreduction and photophosphorylation measured in the presence of ferricyanide showed 50% inhibition at 2×10^–5 M DDT and DDE. P/2e ratios were 1·2–1·5, and remained constant in the presence of both inhibitors. The addition of uncouplers such as ammonium ion and carbonyl cyanide,m-chlorophenylhydrazone did not overcome the inhibition of the chlorinated hydrocarbons. Inhibition of phenazine methosulfate-catalyzed cyclic photophosphorylation by DDT and DDE was observed at low light intensities but was not seen at 2·5×10⁵ erg cm^–2sec^–1 and above. In the presence of DDT, a slow rise in measuring beam fluorescence was observed. The actinic beam fluorescence was slightly less than that in the control. Inhibition by DDT and DDE appears to be similar to that of DCMU. Brief sonication of the chloroplasts increases the sensitivity to DDT. The lack of penetration of DDT to terrestrial plant chloroplasts may be the reason why these are protected from this insecticide.     

Diel changes in DDT absorption and breakdown rates and respiratory rhythm in the housefly, Musca domestica

Absorption rates in three strains of housefly show little variation when DDT is applied at different times during the 24-hr cycle. Rates of breakdown of DDT to DDE, however, vary significantly at different times of the day with most rapid breakdown at 05.00–05.30 and 15.00 hr, corresponding to diel peaks in oxygen consumption. The pre-dawn peak breakdown rates occur at the times at which the flies were found, previously, to be most susceptible to DDT, thus this change in susceptibility must have other causes.

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Zusammenfassung Die Geschwindigkeit, mit der DDT von drei Stubenfliegenrassen absorbiert wurde, zeigte nur wenig Verschiedenheit, wenn es zu verschiedenen Zeiten im Verlauf des 24-h-Tages appliziert wurde. Die Rate des Abbaus von DDT zu DDE variierte dagegen im Lauf des Tages, sie war am grössten um 5.00 bis 5.30 Uhr und um 15.00 Uhr, entsprechend den Tagesspitzen des Sauerstoff-Verbrauchs. Das erste Abbaumaximum (vor Tagesanbruch) fiel zusammen mit der Zeit, in der die Fliegen höchste Empfindlichkeit gegenüber DDT zeigten (vgl. vorige Veröffentlichung). Diese tageszeitspezifische Empfindlichkeit liess sich demnach keineswegs mit einer (geringeren) Abbaugeschwindigkeit in Zusammenhang bringen.

     

Distribution of DDT residues (DDT,DDD, and DDE) in California soils

DDT residues (DDT, DDD, and DDE, or DDT_R) occur in detectable concentrations in soils from southern California over 20 years after a ban (1973) on the widespread use of the pesticide in the U.S. A comparison of DDT residues found in soils from western Riverside/San Bernardino Counties to a much larger statewide database of Mischke et al. (1985) suggests that a systematic regional variation in relative abundances of DDT_R exists in California soils. It is suggested that factors such as physical/chemical properties of DDT residues, local/regional soil‐forming processes, soil management practices, and climatological regimes may help to explain the observed relative abundances of DDT‐related species in California soils. Knowledge of regional trends in the concentrations and composition of soil DDT_R may be useful in formulating more rational risk‐based soil management strategies where soil DDT_R concentrations are at or above regulatory levels.     

Tissue Residue Guideline for ∑DDT for Protection of Aquatic Birds in China

DDT (1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane) is a chlorinated hydrocarbon insecticide that has been used worldwide. While the use of DDT has been phased out in many countries, it is still produced in some parts of the world for use to control vectors of malaria. DDE (1,1,-dichloro-2,2-bis(p-chlorophenyl)ethylene) and DDD (1,1-trichloro-2,2-bis(p-chlorophenyl)ethane) are primary metabolites of DDT and have similar chemical and physical properties. DDT and its metabolites (DDE and DDD) are collectively referred to as ∑DDT. The lipophilic nature and persistence of the ∑DDT result in biomagnification in wildlife that feed at higher trophic levels in the food chain. Wildlife in aquatic ecosystems depend on aquatic biota as their primary source of food, which provide the main route of exposure to ∑DDT. Studies about effects of ∑DDT on birds were reviewed. The tissue residue guidelines for DDT (TRGs) for protection of birds in China were derived using species sensitivity distribution (SSD) and toxicity percentile rank method (TPRM) based on the available toxicity data. Risks of ∑DDT to birds were assessed by comparing the TRGs and ∑DDT concentrations in fishes from China. The tissue residue guideline for protection of birds in China is recommended to be 12.0 ng ∑DDT/g food.     

Dichlorodiphenyldichloroethylene potentiates the effect of protein kinase A pathway activators on progesterone synthesis in cultured porcine granulosa cells.

The insecticide dichlorodiphenyltrichloroethane (DDT) and its major metabolite p,p'-dichlorodiphenyldichloroethylene (DDE) have been implicated as endocrine-modulating chemicals. The DDT metabolite p, p'-DDE has been found contaminating human tissues and follicular fluid because of dietary exposure. We investigated the effects of DDE on progesterone synthesis in a stable porcine granulosa cell line, JC-410, and in primary cultures of porcine granulosa cells. Progesterone synthesis was not affected by 0.1-100 ng/ml DDE in the JC-410 cells. However, 10 ng/ml DDE increased 8-bromo-cAMP (8-Br-cAMP)-stimulated progesterone synthesis 0.4-fold (P < 0.05) over the levels observed with 1 mM 8-Br-cAMP alone. The effect of cholera toxin (CT) on progesterone synthesis was increased 0.7-fold (P < 0.05) by 10 ng/ml DDE over the value observed with 30 ng/ml CT alone. In primary cultures of porcine granulosa cells, 10 ng/ml DDE potentiated CT-stimulated progesterone synthesis 1.2-fold over the value observed with CT alone. In the JC-410 cells, 1 and 10 ng/ml DDE increased CT-stimulated cytochrome P450-cholesterol side-chain cleavage (P450(scc)) mRNA levels 0.3- and 0.4-fold, respectively, over the values obtained with CT alone. Neither basal nor CT-stimulated cAMP levels were changed by DDE. We conclude that DDE affects granulosa cell response to protein kinase A activators by altering the expression of the P450(scc) gene.