A novel open channel blocker of GABA-A receptors

GABA-A receptors are chloride ion channels composed of five subunits, mediating fast synaptic and tonic inhibition in the mammalian brain. 19 different subunit isoforms have been identified, with the major receptor type in mammalian adult brain consisting of α1, β2, and γ2 subunits. GABA-A receptors are the target of numerous sedating and anxiolytic drugs such as benzodiazepines. The currently known endogenous ligands are GABA, neurosteroids and the endocannabinoid 2- arachidonoyl glycerol (2-AG). The pharmacological properties of this chloride ion channel strictly depend on receptor subunit composition and arrangement. GABA-A receptors bind and are inhibited by epileptogenic agents such as picrotoxin, and cyclodiene insecticides such as dieldrin. We screened aromatic monovalent anions with five-fold symmetry for inhibition of GABA-A receptors. One of the anions, PCCPinhibited currents elicited by GABA with comparable potency as picrotoxin. This inhibition showed all characteristics of an open channel block. The GABA-A receptor ion channel is lined by residues from the M2 membrane-spanning segment. To identify important residues of the pore involved in the interaction with the blocking molecules PCCP-, a mutation scan was performed in combination with subsequent analysis of the expressed mutant proteins using electrophysiological techniques. In a second project we characterised a light-switchable modulator of GABA-A receptors based on propofol. It was my responsibility to investigate the switching kinetics in patch clamp experiments. After its discovery in 1980, propofol has become the most widely used intravenous general anaesthetic. It is commonly accepted that the anaesthesia induced by this unusually lipophilic drug mostly results from potentiation of GABA induced currents. While GABA-A receptors respond to a variety of ligands, they are normally not sensitive towards light. This light sensitivity could be indirectly achieved by using modulators that can be optically switched between an active and an inactive form. We tested an azobenzene derivative of propofol where an aryldiazene unit is directly coupled to the pharmacophore. This molecule was termed azopropofol (AP2). The effect of AP2 on Cl- currents was investigated with electrophysiological techniques using α1β2γ2 GABA-A receptors expressed in Xenopus oocytes and HEK-cells. In the third project we wanted to investigate the functional role of GABA-A receptors in the liver, and their possible involvement in cell proliferation. GABA-A receptors are also found in a wide range of peripheral tissues, including parts of the peripheral nervous system and non-neural tissues such as smooth muscle, the female reproductive system, liver and several cancer tissues. However their precise function in non neuronal or cancerous cells is still unknown. For this purpose we investigated expression, localization and function of the hepatocytes GABA-A receptors in model cell lines and healthy and cancerous hepatocytes.

Resisting infection by Plasmodium berghei increases the sensitivity of the malaria vector Anopheles gambiae to DDT

BACKGROUND The evolution of insecticide resistance threatens current malaria control methods, which rely heavily on chemical insecticides. The magnitude of the threat will be determined by the phenotypic expression of resistance in those mosquitoes that can transmit malaria. These differ from the majority of the mosquito population in two main ways; they carry sporozoites (the infectious stage of the Plasmodium parasite) and they are relatively old, as they need to survive the development period of the malaria parasite. This study examines the effects of infection by Plasmodium berghei and of mosquito age on the sensitivity to DDT in a DDT-resistant strain of Anopheles gambiae. METHODS DDT-resistant Anopheles gambiae (ZANU) mosquitoes received a blood meal from either a mouse infected with Plasmodium berghei or an uninfected mouse. 10 and 19 days post blood meal the mosquitoes were exposed to 2%, 1% or 0% DDT using WHO test kits. 24 hrs after exposure, mortality and Plasmodium infection status of the mosquitoes were recorded. RESULTS Sensitivity to DDT increased with the mosquitoes' age and was higher in mosquitoes that had fed on Plasmodium-infected mice than in those that had not been exposed to the parasite. The latter effect was mainly due to the high sensitivity of mosquitoes that had fed on an infected mouse but were not themselves infected, while the sensitivity to DDT was only slightly higher in mosquitoes infected by Plasmodium than in those that had fed on an uninfected mouse. CONCLUSIONS The observed pattern indicates a cost of parasite-resistance. It suggests that, in addition to the detrimental effect of insecticide-resistance on control, the continued use of insecticides in a population of insecticide-resistant mosquitoes could select mosquitoes to be more susceptible to Plasmodium infection, thus further decreasing the efficacy of the control.

STUDIES OF DISULFOTON TOLERANCE IN RATS

Disulfoton (O,O, diethyl S-2-(ethylthio)ethyl phosphorodithioate) and other organophosphorus ester compounds are insecticides which inhibit acetylcholinesterase. Chemicals of this class cause signs of toxicity in mammals which are referable to acculmulation of acetylcholine at neuroeffector sites. A tolerance to this toxic action can be induced in experimental animals by giving multiple, sublethal doses of the compounds. There is strong evidence that disulfoton tolerance occurs because of a reduction in the sensitivity of tissues in the affected animals to acetylcholine.^ Experiments were designed to test the possibility that a decrease in the number of muscarinic cholinergic receptors could be downmodulating the sensitivity of tissues to acetylcholine. It was found that, concomitant with the onset of disulfoton tolerance, there was a decrease relative to control values in the specific binding of {('3)H} quinuclidinyl benzilate ({('3)H}QNB, a compound which selectively labels muscarinic cholinergic receptors) to homogenates of rat brain and ileal muscle. The decrease in {('3)H}QNB binding was due to a reduction in the density of muscarinic receptors. There was, however, no alteration in the binding of {('3)H} QNB, or the muscarinic agonists {('3)H} oxotremorine-M and oxotremorine to atria from disulfoton-tolerant rats. The possibility that cardiac tissue was not subsensitive to cholinergic agonists was ruled out in experiments testing the effect of the muscarinic agonist carbachol on heart rate in vivo, and the negative chronotropic effect of oxotremorine on atria from disulfoton-tolerant rats: a clear reduction in the sensitivity to cholinergic agonists was seen in each case. It was, therefore concluded that the specificity and temporal correlation of {('3)H}QNB binding decreases suggested that the loss of muscarinic receptors might play a role in modulating the sensitivity of several tissues to acetylcholine, but that other mechanisms also contribute to the tolerance phenomenon.^ Other experiments revealed that disulfoton tolerance, as measured by resistance to the lethal effects of carbachol, could be induced by feeding rats low levels of the organophosphorus ester in the diet. The concentration of disulfoton used inhibited acetylcholinesterase, but not to the extent that overt signs of toxicity were observed. These results suggested that tolerance to organophosphorus ester insecticides could be induced in rodents with a dosing scheme which more closely modeled the sort of low level exposures which would be expected in humans environmentally or occupationally in contact with these compounds. ^

MECHANISMS OF SPECIES DIFFERENCES IN BRAIN ACETYLCHOLINESTERASE SENSITIVITY TO ORGANOPHOSPHATE INHIBITION

In vitro incubation of acetylcholinesterase from brain tissue of several species with organophosphate compounds indicated that the concentrations required to inhibit 50% of acetylcholinesterase activity (IC(,50)) differed from species to species for the same compound (Murphy, et al., 1968; Andersen, et al., 1972, 1977 and 1978).^ The hypothesis that non-specific binding proteins (Lauwerys and Murphy, 1969a,b) exerts a protective effect on acetylcholinesterase, and thus cause the differences observed in IC(,50) studies was tested by a ('3)H-DFP binding experiment. It was found that differences in the amount of non-specific binding protein cannot explain the observed differences observed in IC(,50) studies.^ An alternative hypothesis, that acetylcholinesterase from different species have different affinities for binding and/or different rates of phosphorylation by organophosphate insecticides was tested by determining the apparent affinity constant (k(,a)) and apparent rate of phosphorylation (k(,p)). Kinetic studies indicated that acetylcholinesterases from different species have different sensitivities to inhibition by organophosphate insecticides, and the differences are due to different affinities for binding and/or different rates of phosphorylation by the same organophosphate compound.^ Studies of the spontaneous reactivation of acetylcholinesterase after inhibition by organophosphate insecticides also indicated that acetylcholinesterases from different species have different rates and extents of spontaneous reactivation. This further substantiates the hypothesis that acetylcholinesterases from different species have different kinetic characteristics with respect to organophosphate insecticides inhibition.^ Eleven paraoxon analogs were synthesized for a quantitative structure-activity relationship study. It was found that the electron-withdrawing power ((sigma)) and hydrophobicity ((PARAGR)) of the substituent are important in determining the anti-cholinesterase activity of paraoxon analogs. Thus, predictions of species differences in acetylcholinesterase sensitivities to paraoxon analogs can be made if the physicochemical parameters ((sigma) and (PARAGR)) of the substituents are known.^ In another approach, i.e. enzyme modeling, the sensitivity of rat brain acetylcholinesterase to organophosphate insecticides was used as the independent variable to predict the sensitivities of acetylcholinesterases from other species to the same compound. Regression equations were derived for each species based on nineteen organophosphate insecticides studied. It was found, that in addition to paraoxon analogs, this method is also applicable to other organophosphate compounds with wide variations in structure. Thus, the sensitivities of acetylcholinesterases from other species can also be predicted from the sensitivity of rat brain acetylcholinesterase. ^

Lindane induced cellular dysfunction in MDCK cells: The role of the peripheral benzodiazepine receptor

The central nervous system GABAA/Benzodiazepine (GABAA/BZD) receptors are targets for many pharmaceutical agents and several classes of pesticides. Lindane is an organochlorine pesticide, although banned from production in the U.S. since 1977, still imported for use as an insecticide and pharmaceutically to control ectoparasites (ATSDR, 1994). Lindane functions as a GABA/BZD receptor antagonist within the central nervous system (CNS). Outside of the CNS, peripheral BZD receptors have been localized to the distal tubule of the kidney. Previous research in our laboratory has shown that incubation of renal cortical slices with lindane can produce an increase in kallikrein leakage, suggesting a distal tubular effect. In this study, Madin Darby Canine Kidney (MDCK) cells were used as an in vitro system to assess the toxicity of lindane. This purpose of this study was to determine if interactions between a renal distal tubular BZD-like receptor and lindane could lead to perturbations in renal distal cellular chloride (Cl−) transport and mitochondrial dysfunction and ultimately, cellular death. ^ Pertubations in renal chloride transport were measured indirectly by determining if lindane altered cell function responsiveness following osmotic stress. MDCK cells pre-treated with lindane and then subjected to osmotic stress remained swollen for up to 12 hours post-stress. Lindane-induced dysfunction was assessed through stress protein induction measured by Western Blot analysis. Lindane pretreatment delayed Heat Shock Protein 72 (HSP72) induction by 36 hours in osmotically stressed cells. Pretreatment with 1 × 10 −5 M LIN followed by osmotic stress elevated p38 and Stress Activated Protein Kinase (SAPK/JNK) at 15 minutes which declined at 30 minutes. Lindane appeared to have no effect on Endoplasmic Reticulum Related Kinase (ERK) induction. Lindane did not effect osmotically stressed LLC-PKI cells, a control cell line. ^ Lindane-treated MDCK cells did not exhibit necrosis. Instead, apoptosis was observed in lindane-treated MDCK cells in both time- and dose-dependent manners. LLC-PKI cells were not affected by LIN treatment. ^ To better understand the mechanism of lindane-induced apoptosis, mitochondrial function was measured. No changes in cytochrome c release or mitochondrial membrane potential were observed suggesting the mitochondrial pathway was not involved in lindane-induced apoptosis. ^ Further research will need to be conducted to determine the mechanism of lindane-induced adverse cellular effects. ^

Evaluation of oxidative damage and renal distal tubule cell stress response following exposure to lindane

Lindane, or γ-hexachlorocyclohexane, is a chlorinated hydrocarbon pesticide that was banned from U.S. production in 1976, but until recently continued to be imported and applied for occupational and domestic purposes. Lindane is known to cause central nervous system (CNS), immune, cardiovascular, reproductive, liver, and kidney toxicity. The mechanism for which lindane interacts with the CNS has been elucidated, and involves antagonism of the γ-aminobutyric acid/benzodiazepine (GABAA/BZD) receptor. Antagonism of this receptor results in the inhibition of Cl- channel flux, with subsequent convulsions, seizures, and paralysis. This response makes lindane a desirable defense against arthropod pests in agriculture and the home. However, formulation and application of this compound can contribute to human toxicity. In conjunction with this exposure scenario, workers may be subject to both heat and physical stress that may increase their susceptibility to pesticide toxicity by altering their cellular stress response. The kidneys are responsible for maintaining osmotic homeostasis, and are exposed to agents that undergo urinary excretion. The mechanistic action of lindane on the kidneys is not well understood. Lindane, in other organ systems, has been shown to cause cellular damage by generation of free radicals and oxidative stress. Previous research in our laboratory has shown that lindane causes apoptosis in distal tubule cells, and delays renal stress response under hypertonic stress. Characterizing the mechanism of action of lindane under conditions of physiologic stress is necessary to understand the potential hazard cyclodiene pesticides and other organochlorine compounds pose to exposed individuals under baseline conditions, as well as under conditions of physiologic stress. We demonstrated that exposure to lindane results in oxidative damage and dysregulation of glutathione response in renal distal tubule (MDCK) cells. We showed that under conditions of hypertonic stress, lindane-induced oxidative stress resulted in early onset apoptosis and corresponding down-regulated expression of the anti-apoptotic protein, Bcl-xL. Thus, the interaction of lindane with renal peripheral benzodiazepine receptors (PBR) is associated with attenuation of cellular protective proteins, making the cell more susceptible to injury or death. ^

RESPONSES OF INDICATOR AND PATHOGENIC BACTERIA TO THE PRESENCE OF CARBARYL IN WATER

Biodegradability is a desirable, if not a necessary characteristic of pesticides. Carbaryl, as Sevin, is one of the more widely used insecticides for the control of agricultural pests and has been reported to be readily degraded by microorganisms. Because of its broad application, the concentration of Sevin in surface waters has been reported to reach nearly four parts per million (PPM) in surface waters, where it has been reported to affect the growth and metabolic rates of aquatic bacterial populations. Following these reports, it is of public health importance to determine the effects of this insecticide on the growth and metabolic rates of bacteria used to indicate water pollution, and on pathogenic organisms which are found in polluted water.^ This study was conducted to determine the effect of carbaryl on the growth and metabolic rates of indicator and pathogenic organisms. Escherichia coli and Streptococcus faecalis were used as indicators, while Staphylococcus aureus and Salmonella typhimurium were the pathogens studied. Pure and mixed cultures of these organisms were exposed to two concentrations of carbaryl (Sevin).^ The study demonstrated that the fecal pollution indicator organisms, E. coli and S. faecalis respond differently to the presence of small concentrations of carbaryl in water as do the two pathogens tested, (S. typhimurium and S. aureus). The growth of all test organisms as measured by spread plate counts, was reduced by the presence of either one mg/l or five mg/l carbaryl within a period of eight days. Survival of the organisms in the presence of five mg/l carbaryl varied dependent upon whether the organism was in pure or mixed culture. In the presence of five mg/l carbaryl, both pure and mixed culture of E. coli showed longer survival. S. faecalis survived for more than eight days in pure culture, neither S. typhimurium nor S. aureus survived for eight days in pure culture.^ The metabolic rate of S. faecalis and S. aureus was reduced by both five mg/l and one mg/l Sevin concentrations, contrary to E. coli and S. typhimurium which had reduced metabolic rate with the introduction of five mg/l Sevin but showed an increase in the metabolic rate with one mg/l Sevin. There was no difference between the test and control when mixed populations were exposed to five mg/l Sevin and the metabolic rate tested. A mixture of E. coli and S. typhimurium populations showed a respiration increase over the control when exposed to one mg/l Sevin concentration. If similar effects occur in polluted surface waters, misleading results from bacteriological water quality testing may occur. ^

Controlling Bacterial Wilt in Muskmelon with Perimeter Trap Cropping

Perimeter trap cropping (PTC) involves planting one or more rows of a cucurbit crop that is highly attractive to cucumber beetles around the border of a main cucurbit cash crop that is less attractive to the beetles. Cucumber beetles attempting to migrate into the field are concentrated in the relatively more attractive border crop, where they can be controlled by insecticides. In New England, perimeter trap cropping using Blue Hubbard squash as the border crop around pumpkin, cucumber, or butternut squash controlled cucumber beetle/bacterial wilt with as few as one border spray of insecticide. This strategy reduced insecticide use on the main crop by up to 94 percent, nearly eliminating sprays on the main cash crop. In on-farm trials, 8 of 10 Massachusetts growers found that using perimeter trap cropping saved them money. The same tactic also effectively managed cucumber beetles on muskmelon and squash in Oklahoma.

Organic Practices for the Production of Butternut Squash

Growers of organic squash need effective ways to manage insect and disease problems. The squash bug (Anasa tristis) sucks sap, causing leaves to wilt and turn black. The squash vine borer (Melittia cucurbitae) can devastate winter squash plantings. Burrowing by larvae into the base of the stem causes yellowing and wilting. Organic insecticides are expensive, have limited efficacy, require many applications, and some kill beneficial as well as target insects.

Actividad insecticida de Ricinus Communis L. sobre Plodia Interpunctella Hbn. (Lepidoptera: Phycitinae).

La aplicación de insecticidas sintéticos como principal sistema de control de plagas de granos y productos almacenados ha originado el desarrollo de poblaciones de insectos resistentes a dichos químicos, la contaminación del medio ambiente y la acumulación de sustancias tóxicas en los alimentos. En este trabajo se evaluaron los efectos de la aplicación de molido de hojas de ricino sobre larvas de la «polilla de las harinas» (Lepidoptera: Phycitinae). Los molidos vegetales se obtuvieron a partir de hojas de Ricinus communis L. secadas en estufa a 40 ± 2 °C durante 48 horas y posteriormente molidas hasta lograr un polvo de textura similar a la harina de maíz, material con el que se mezcló a fin de lograr concentraciones de 5, 10 y 15 % y un testigo sin ricino. Las unidades experimentales consistieron en cajas de Petri con seis larvas de primer y segundo estadio y se efectuaron cinco repeticiones por tratamiento (n=120). Se registró el número de larvas, pupas y adultos vivos, cada cuatro días, hasta que las larvas sobrevivientes llegaron al estado adulto. Se calcularon los porcentajes de eficacia mediante la fórmula de Abbott. Los resultados se evaluaron por ANVA y test de Tukey. Se determinaron el tiempo efectivo medio (TE50) y concentración efectiva media (CE50) por el método Probit. Los resultados de mortalidad indicaron que la concentración al 15 % superó significativamente al resto de los tratamientos y al testigo.

Eficiencia de control de "orugas defoliadoras" en soja (Glycine max L.), con insecticidas neurotóxicos y reguladores del crecimiento de los insectos

Las "orugas defoliadoras" afectan la producción del cultivo de soja, sobre todo en años secos y con altas temperaturas que favorecen su desarrollo. El objetivo del presente trabajo fue evaluar la eficiencia de control de insecticidas neurotóxicos e IGRs sobre "orugas defoliadoras" en soja. Se realizaron ensayos en lotes comerciales en tres localidades de la provincia de Córdoba en las campañas agrícolas 2008/09 y 2009/10, bajo un diseño de bloques al azar, con seis tratamientos y tres repeticiones. Los tratamientos fueron: T1: Clorpirifos (384 g p.a.ha-1), T2: Cipermetrina (37,5 g p.a.ha-1), T3: Lufenuron+Profenofos (15 + 150 g p.a.ha-1), T4: Metoxifenocide (28,8 g p.a.ha-1), T5: Novaluron (10 g p.a.ha-1) y T6: Testigo. El tamaño de las parcelas fue de 12 surcos de 10 m de largo distanciados a 0,52 m. La aplicación se realizó con una mochila provista de boquillas de cono hueco (40 gotas.cm-2), cuando la plaga alcanzó el umbral de daño económico. En cada parcela se tomaron cinco muestras a los 0, 2, 7 y 14 días después de la aplicación (DDA) utilizando el paño vertical, identificando y cuantificando las orugas vivas mayores a 1,5 cm. A los 14 DDA se extrajeron 30 folíolos por parcela (estrato medio y superior de la planta) y se determinó el porcentaje de defoliación utilizando el software WinFolia Reg. 2004. Se estimó el rendimiento sobre 5 muestras de 1 m2 en cada parcela y se realizó ANOVA y test de comparación de medias LSD de Fisher. El Clorpirifos mostró el mayor poder de volteo y el Metoxifenocide la mayor eficiencia a los 7 DDA. En general los IGRs mostraron mayor poder residual.

Egg parasitism of Piezodorus guildinii and Nezara viridula (Hemiptera: Pentatomidae) in soybean, alfalfa and red clover

Piezodorus guildinii Westwood and Nezara viridula (L.) (Hemiptera: Pentatomidae) are important soybean pests. P. guildinii causes more injury and is less susceptible to insecticides compared to N. viridula. N. viridula egg parasitoids are well studied; however, little is known about parasitoids of P. guildinii. Alfalfa, soybean and red clover were sampled during several seasons to characterize the abundance of both stink bugs, to determine their egg parasitoids, and to estimate parasitoids impact. In the field, Telenomus podisi (Ashmead),Trissolcus urichi (Crawford) and Trissolcus basalis (Wollaston) (Hymenoptera: Platygastridae) emerged from P. guildinii, while only T. basalis (Wollaston) (Hymenoptera: Platygastridae) emerged from N. viridula. The proportions of parasitized eggs (i. e., the parasitoid impact) and egg masses, as well as the number of parasitized eggs/total number of eggs of the parasitized egg masses, were similar for alfalfa and soybean. Parasitism was not observed in red pclover. Parasitoid impact was lower during the dry growing seasons. Although P. guildinii field parasitism by T. urichi was less significant, laboratory experiments from the bibliography indicate that this wasp species performs well on this host. Trissolcus urichi would be an important biological control agent against P. guildinii, principally when the stink bug is more abundant.

(Table 1) Enantiomer fractions of egg yolk and plasma samples from Svalbard glaucous gulls (Larus hyperboreus)

Glaucous gulls (Larus hyperboreus) and their eggs from Svalbard (Norwegian Arctic) have been used as biomonitors of contaminants in the marine environment. In this study, the enantiomer fractions (EFs) of chiral chlordanes and atropisomeric polychlorinated biphenyl (PCB) congeners were determined in the blood plasma of adult male and female glaucous gulls from three breeding colonies in Svalbard. Plasma EFs were similar in magnitude and direction to EFs previously reported in glaucous gulls from other arctic food webs, suggesting overall similarities in the biochemical processes influencing the EFs of bioaccumulated organochlorine (OC) contaminants within the food webs at those locations. Additionally, EFs in yolk of eggs collected concurrently from within the same nesting colonies varied with location, laying date, and OC concentrations, and may be influenced by changes in the local feeding ecology between those colonies. No differences were found between the EFs for any analyte in female gulls compared to those found in egg yolk, indicating that processes involved in the maternal transfer of chlordanes and PCBs to eggs do not modulate the stereochemical ratio between enantiomers. Therefore, the use of eggs as a valuable and noninvasive means of OC biomonitoring may also extend to enantiomer compositions in glaucous gulls, and perhaps also in other seabird species from arctic regions.

(Table 1) Circulating levels of TT3 and TT4, and age, length, girth, and estimated body mass in polar bears (Ursus maritimus) from East Greenland 1999-2001

We investigated the multivariate relationships between adipose tissue residue levels of 48 individual organohalogen contaminants (OHCs) and circulating thyroid hormone (TH) levels in polar bears (Ursus maritimus) from East Greenland (1999-2001, n = 62), using projection to latent structure (PLS) regression for four groupings of polar bears; subadults (SubA), adult females with cubs (AdF_N), adult females without cubs (AdF_S) and adult males (AdM). In the resulting significant PLS models for SubA, AdF_N and AdF_S, some OHCs were especially important in explaining variations in circulating TH levels: polybrominated diphenylether (PBDE)-99, PBDE-100, PBDE-153, polychlorinated biphenyl (PCB)-52, PCB-118, cis-nonachlor, trans-nonachlor, trichlorobenzene (TCB) and pentachlorobenzene (QCB), and both negative and positive relationships with THs were found. In addition, the models revealed that DDTs had a positive influence on total 3,5,3'-triiodothyronine (TT3) in AdF_S, and that a group of 17 higher chlorinated ortho-PCBs had a positive influence on total 3,5,3',5'-tetraiodothyronine (thyroxine, TT4) in AdF_N. TH levels in AdM seemed less influenced by OHCs because of non-significant PLS models. TH levels were also influenced by biological factors such as age, sex, body size, lipid content of adipose tissue and sampling date. When controlling for biological variables, the major relationships from the PLS models for SubA, AdF_N and AdF_S were found significant in partial correlations. The most important OHCs that influenced TH levels in the significant PLS models may potentially act through similar mechanisms on the hypothalamic-pituitary-thyroid (HPT) axis, suggesting that both combined effects by dose and response addition and perhaps synergistic potentiation may be a possibility in these polar bears. Statistical associations are not evidence per se of biological cause-effect relationships. Still, the results of the present study indicate that OHCs may affect circulating TH levels in East Greenland polar bears, adding to the "weight of evidence" suggesting that OHCs might interfere with thyroid homeostasis in polar bears.

(Table 1) Concentrations of persistant organic pollutants in brain and liver of glaucous gulls, Bjørnøya, Svalbard archipelago

Dead and dying glaucous gulls (Larus hyperboreus) were collected on Bjornoya in the Barents Sea in 2003, 2004 and 2005. Autopsies of the seabirds only explained a clear cause of death for three (14%) of the 21 birds. A total of 71% of the birds were emaciated. Liver and brain samples were analysed for organochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), polybrominated diphenyl ether (PBDEs), hexabromo-cyclododecanes (HBCDs) and mercury (Hg). High levels of OCPs, PCBs, PBDEs and alpha-HBCD were found in liver and brain. Compared to the dead and dying glaucous gulls found 1989, the congeners' composition tended to change toward more persistent compounds in the 2003-2005 samples. The brain levels of OCPs and PCBs did not differ between 1989 and 2003-2005, while the liver levels were significantly lower. The brain/liver ratio for PCB and PBDE significantly decreased with halogenations of the molecule, indicating a clear discrimination of highly halogenated PCBs and PBDEs entering the brain. There was further a clear negative correlation between contaminant concentrations and body condition. The brain levels were not as high as earlier published lethal levels of p,p'-DDE or PCB. However, more recent studies reported a range of sub-lethal OCP- and PCB-related effects in randomly sampled glaucous gulls. An additional elevation of pollutants due to emaciation may increase the stress of the already affected birds. The high brain levels of OCP, PCB and PBDE of present study might therefore have contributed to the death of weakened individuals of glaucous gull.