Pesticide-induced changes in hepatic microsomal enzyme systems: further studies on the effects of 1,1,-di(p-chlorophenyl)-2-chloroethylene (DDMU) in the Japanese quail

Brominated flame retardants, polychlorinated biphenyls, and organochlorine pesticides in bird eggs from the Yellow River Delta, North China

Concentrations of several persistent organohalogen compounds such as dichlorodiphenyltrichloroethane and its metabolites (DDTs), hexachlorocyclohexanes (HCHs), polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), decabromodiphenylethane (DBDPE), and polybrominated biphenyl 153 (PBB 153) were measured in eggs of six species of wild aquatic birds, one species of wild terrestrial bird, and two species of captive birds from North China. Among the contaminants measured, DDTs were the dominant compounds, HCHs and PCBs were in nearly the same concentration range, and PBDEs exhibited lower concentrations than other compound groups. The median concentrations of DDTs, HCHs, PCBs, and PBDEs in all avian species ranged from 21 to 11034, 5.5 to 623, 1.0 to 613, and 4.6 to 146 ng/g lipid wt, respectively. Median concentrations of DBDPE and PBB 153 in all avian species were in the range of not detectable (ND)-1.7 and ND-0.7 ng/g lipid wt, respectively. Significant differences among species in contaminant profiles and contaminant levels were found depending on their feeding habits, habitat, and migration. The captive birds had the lowest contaminant levels and entirely different congener profiles in PCBs and PBDEs from those of wild birds, which can be attributed to differences in dietary compositions and reproduction rates. Octa- to deca-BDEs contributed more to the total PBDEs in wild terrestrial and captive birds than in wild aquatic birds, except for one insectivorous species, possibly due to greater exposure to terrestrial food sources. Preliminary risk assessment suggests that there is no risk of a reduction in offspring survival in avian species from North China due to organohalogen compounds, except for dichlorodiphenyldichloroethylene (DDE), which would be expected to affect some proportion of the populations of several species of birds studied.

Occurrence and fate of 1-chloro-2,2-bis(4-chlorophenyl)ethene in the environment of the Pearl River Delta, South China

1-Chloro-2,2-bis(4-chlorophenyl)ethene (p,p'-DDMU), a metabolite of either 1,1-dichloro-22-bis(4-chlorophenyl)ethane (p,p'-DDD) or 1,1-dichloro-2,2-bis(4-chlorophenyl)ethene (p,p'-DDE), which is degraded from 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (p,p'-DDT), was detected in a variety of environmental matrices of the Pearl River Delta (PRD), South China, including fish, fish feeds, semidigested fish stomach contents, marine surface sediment, surface soil, atmospheric gaseous phase, and particulates, rainwater, and coastal rainwater. Forfish species,the concentrations of p,p'-DDMU were significantly higher in farmed fish than in marine wild fish, with the highest value obtained in seawater farmed fish species (mear/median values of 262/173 ng/g lipid). The relative abundance of p,p'-DDMU to total DDTs (sum of o,p'- and p,p'-DDT, DDD, and DDE) was higher in samples of marine origin (approximately 5%) than in those of terrestrial origin (approximately 2%). Because p,p'-DDD was considerably abundant in all samples and a negative linear correlation was found between p,p'-DDD/(p,p'-DDD + p,p'-DDE) and p,p'-DDMU/DDTs in the marine sediments (r2 = 0.73) and seawater farmed fish (r2 = 0.29) under investigation, it is possible that DDMU was partially dehydrochlorinated from DDD in the environment of the PRD. A fugacity-based assessment suggested that p,p'-DDMU is likely to transport from sediment to seawater and then to air and from soilto air. The ubiquity of p,p'-DDMU in the PRD indicates that it may also be widespread worldwide particularly in countries with large amounts of DDT used currently and/or historically. Given the potential risk of p,p'-DDMU to human health, more efforts should be directed toward to this previously overlooked contaminant

The effects of 1,1-di(p-chlorophenyl)-2-chloroethylene (DDMU) on hepatic morphology of Japanese quail

The effects of dietary administration of 1,1-di(p-chlorophenyl)-2-chloroethylene (DDMU) to Japanese quail at a concentration of 100 ppm were investigated for periods of up to 32 days. Hepatic morphology was studied by light microscopy. Histologic changes observed included cytoplasmic and nuclear degeneration in the hepatocytes followed by severe lipid accumulation and hepatocellular hypertrophy. There was a progressive increase in cytoplasmic vacuoles containing lipid up to Day 24 followed by a decrease by Day 32 when the numbers of vacuoles remained greater than those in untreated quail livers. The vacuoles showed a distribution which followed the functional acinar units of the liver. Increased numbers and hypertrophy were observed in Kupffer cells and fibrocytes. There was an occasional necrotic hepatocyte observed but this lesion was not a prominent feature. Hepatocellular hyperplasia occurred as the lipid accumulation decreased. The histologic findings are compared with the biphasic response previously described.

Species differences in the effects of 1,1-di-(4-chlorophenyl)-2-chloroethylene (DDMU) and 1,1-di-(4-chlorophenyl)-2,2-dichloroethylene (DDE) on glutathione levels in isolated hepatocytes from Japanese quail and rat

1. Hepatocytes have been isolated from adult Japanese quail in high yields (26-40 X 10(6) cells/g) with 95% viability. Variation in the collagenase and hyaluronidase levels and incubation time used in the isolation procedure affected the yield and viability of the hepatocytes. Quail hepatocytes were more stable in a standard nutrient medium than those of the rat. 2 1,1-Di-(4-chlorophenyl)-2-chloroethylene (DDMU), a metabolite of DDT, depleted quail hepatic GSH levels both in vitro and in vivo, but had no effect on rat hepatocytes. DDMU (0.1 mM) depleted GSH levels in the quail to the same extent as diethyl maleate (a known GSH-depleting agent) (0.04 mM) but the latter acted more rapidly. 3. Pretreatment of quail in vivo with DDMU or phenobarbitone, known inducers of the hepatic mixed-function oxidases, resulted in faster depletion of GSH when the hepatocytes were incubated subsequently with DDMU in vitro. 4. In contrast, 1,1-di-(4-chlorophenyl)-2,2-dichloroethylene (DDE), another metabolite of DDT, did not deplete GSH levels in the quail but did cause some reduction in the rat. Phenobarbitone pretreatment had no effect on GSH depletion by DDE in vitro in quail hepatocytes but enhanced GSH depletion in rat hepatocytes.

A study on the toxicity and the biochemical effects of ethylene dibromide in the Japanese quail

1. The acute oral LD50 and chronic LC50 toxicity values for ethylene dibromide (EDB) were estimated for japanese quail. 2. Single sub-acute oral and intraperitoneal doses of EDB (1/2 LD50) and chronic oral doses of EDB (1/3 LC50) were administered to quail in order to characterise the sub-lethal effects of EDB residues. 3. At 24 h after sub-acute dosing, relative liver weight, plasma aspartate aminotransferase (AT) [EC 2.6.1.1] and L-iditol (sorbitol) dehydrogenase (SDH) [EC 1.1.1.14] were elevated and decreases were found in hepatic total lipid, total protein, AT and glutamic dehydrogenase (NAD (P)+) (GDH) and plasma cholinesterase (ChE) [EC 3.1.1.8] and total lipid. 4. Following chronic administration, elevations in relative liver weight, plasma ChE and total lipid, haemoglobin and haematocrit were found and hepatic AT, GDH and total lipid were decreased. 5. The changes in hepatic and plasma enzymes and constituents are discussed in relation to possible biphasic effects resulting from EDB exposure.

The effects of 1,1-di(p-chlorophenyl)-2-chloroethylene on plasma enzymes and blood constituents in the Japanese quail

Glutamate oxaloacetate transminase (GOT), glutamate dehydrogenase (GDH), sorbitol dehydrogenase (SDH), pseudo-cholinesterase (ChE) and various blood constituents were measured in the plasma of Japanese quail fed 1,1-di(p-chlorophenyl)-2-chloroethylene (DDMU) at low levels for periods ranging from 2 to 32 days. Previous work has shown that DDMU is a potent inducer of hepatic microsomal enzymes causing marked structural changes in the liver. A rapid increase in plasma GOT was observed within 4 days accompanied by an increase in relative liver weight. Plasma GDH and SDH increased to a maximum between 16 and 24 dyas which seems to be associated with hepatic cell proliferation. Plasma ChE showed a steady increase over the time course of DDMU administration. The level of plasma lipid was reduced after 4 days whereas the hepatic lipid content was substantially increased suggesting that the fatty liver condition may be caused by decreased release of triglyceride from the liver. Plasma glucose was reduced at 8 days but there was no evidence of a hyperglycaemic state. The changes noted after 2 days of DDMU diet were confirmed by measurements on birds 18 h after oral dosing the DDMU. The study demonstrates the value of plasma enzyme measurements for the early detection of toxic effects and indicates that DDMU administration leads to extrahepatic effects in addition to those previously described in the liver.