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PubMed1983

[Survey On Encysted Cercariae Of Trematodes From Fresh-Water Fishes In Mangyeong Riverside Area]

In order to clarify infestation pattern for the encysted larvae of digenetic trematodes from fresh-water fishes, this survey was carried out from March to September, 1983. A total of 380 fishes of 32 species were collected with netting at the three reaches, upper, middle and lower in Mangyeong riverside area. After the fishes were dissected into small scraps, they were pressed under cover glass and examined for the presence of those of digenetic trematodes with a microscope. The results obtained were as follows: Out of a total of 380 fishes inspected, 320 fishes (84 %) from 31 species were found positive with digenetic trematode metacercariae; more than 10 species of the metacercariae were detected in Pseudorasbora parva; Gnathopogon majimae, Microphysogobio yaluensis, Cultriculus eigenmanni and Gnathopogon coreanus (more than 8 species); Aphyocypris chinensis(8 species) and etc. respectively. Clonorchis sinensis metacercariae were found positive from 93 fishes (25 %) from 12 species detection rates in other species of digenetic trematode metacercariae from various fishes were; Exorchis oviformis, 261 fishes (57 %) from 28 species; Cyathocotyle orientalis, 47 fishes (12 %) from 12 species; Metorchis orientalis, 21 fishes (6 %) from 12 species; Metagonimus yokogawai, 164 fishes (43 %) from 26 species; Pseudexorchis major, 71 fishes (19 %) from 18 species; Metacercaria hasegawai, 77 fishes (20 %) from 25 species; Centrocestus armatus, 24 fishes (6 %) from 7 species; Echinochasmus japonicus, 2 fishes (0.5 %) from 2 species, and unidentified species, 34 fishes (9 %) from 15 species respectively. The sums of average number of the encysted larvae of all species found in fish body/gram showed 83 in P. parva, Cobitis taenia (74.2), A. chinensis (28.5), Pseudoperilampus uyekii (26.6), G. majimae (19.6) and etc. respectively and the average peak number of each metacercaria in fish body/gram showed 21.7 C. sinensis, 24 E. oviformis, 15.3 M. orientalis and 6.1 E. japonicus in P. parva; 42.7 C. orientalis and 25.1 M. yokogawai in C. taenia; 8.3 C. armatus and 8.3 M. hasegawai in P. uyekii; 6.3 P. major in Carassius carassius, and 2.9 unidentified species in G. majimae respectively.

Journal Article↗
PubMed1995

Aspects of the ecology of metazoan ectoparasites of marine fishes.

Numerous (3947) individuals of 102 marine fish species from Papua New Guinea, New Zealand, the North Sea, Antarctica, the deepsea and coast of southeastern Australia, Pacific Canada, Brazil, Argentina and the Great Barrier Reef were examined for metazoan ectoparasites. Of the 102 fish species, 86 harboured at least 1 parasite species, and only in Antarctica and the deepsea were large proportions of fish species found to be free of ectoparasites. The mean prevalence of infection was 30.1%, the average of abundances was 6.7 parasites per fish, due to very heavy intensities of some parasite species (mean median abundance 4.31). Most parasite species exhibited a clustered distribution in the host populations, as measured by variance to mean ratios, i.e. some fish were more, and others less, heavily infected than if infection were random. Core and satellite species cannot be distinguished unambiguously, because numbers of parasites on almost all hosts are too small for any bimodality to become apparent. On average, the most dominant species represented 90% of all parasite individuals of a particular fish; different parasite species were often dominant on different fish individuals of a particular host species. Both abundances and maximum intensities of infection were positively correlated with prevalence of infection. Community richness varies greatly at and between localities, with the lowest richness found in Antarctic and deepsea fish and the highest richness in tropical fish. Species richness, abundance and prevalence of infection in many fish groups (with different ecological characteristics) are strongly correlated with temperature. If fish from all localities were pooled, pelagic fish had fewer intensities and (jointly with benthopelagic fishes) fewer species than benthic fish, and planktivorous fish had lower abundances and prevalences of infection than predatory and omnivorous fish. Prevalences of infection, abundance and parasite species richness were significantly correlated with host length. Fifteen positive and 1 negative associations among species were found. This and the generally low prevalences and abundances of infection indicate that competitive interactions are probably scarce. Overall, the findings indicate that most (if not all) metazoan ectoparasite communities of marine fish live in non-saturated, little-ordered assemblages.

Animals↗
PubMed2005

Environmental contaminants and biomarker responses in fish from the Rio Grande and its U.S. tributaries: spatial and temporal trends.

We collected, examined, and analyzed 368 fish of seven species from 10 sites on rivers of the Rio Grande Basin (RGB) during late 1997 and early 1998 to document temporal and geographic trends in the concentrations of accumulative contaminants and to assess contaminant effects on the fish. Sites were located on the mainstem of the Rio Grande and on the Arroyo Colorado and Pecos River in Texas (TX), New Mexico (NM), and Colorado. Common carp (Cyprinus carpio) and largemouth bass (Micropterus salmoides) were the targeted species. Fish were examined in the field for internal and external visible gross lesions, selected organs were weighed to compute ponderal and organosomatic indices, and samples of tissues and fluids were obtained and preserved for analysis of fish health and reproductive biomarkers. Whole fish from each station were composited by species and gender and analyzed for organochlorine chemical residues and elemental contaminants using instrumental methods, and for 2,3,7,8-tetrachloro dibenzo-p-dioxin-like activity (TCDD-EQ) using the H4IIE rat hepatoma cell bioassay. Overall, fish from lower RGB stations contained greater concentrations of organochlorine pesticide residues and appeared to be less healthy than those from sites in the central and upper parts of the basin, as indicated by a general gradient of residue concentrations and biomarker responses. A minimal number of altered biomarkers and few or no elevated contaminant concentrations were noted in fish from the upper RGB. The exception was elevated concentrations [up to 0.46 microg/g wet-weight (ww)] of total mercury (Hg) in predatory species from the Rio Grande at Elephant Butte Reservoir, NM, a condition documented in previous studies. Arsenic (As) and selenium (Se) concentrations were greatest in fish from sites in the central RGB; Se concentrations in fish from the Pecos River at Red Bluff Lake, TX and from the Rio Grande at Langtry, TX and Amistad International Reservoir, TX exceeded published fish and wildlife toxicity thresholds. In the lower RGB, residues of p,p'-DDT metabolites (<or=1.69 microg/g ww), chlordane-related compounds (<or=0.21 microg/g ww), dieldrin (<or=0.0.05 microg/g ww), and toxaphene (<or=2.4 microg/g ww) were detected in fish from most sites; maximum concentrations were in channel catfish (Ictalurus punctatus) from the Arroyo Colorado at Harlingen, TX. Concentrations of one or more residues exceeded toxicity thresholds for fish and wildlife in fish from this site and from the Rio Grande at Mission, TX and Brownsville, TX; however, concentrations were lower than those reported by previous studies. In addition, the proportional concentrations of p,p'-DDT at all sites were low, indicating weathered DDT rather than the influx of new material. Concentrations of total PCBs (<0.05 microg/g ww) and TCDD-EQ (<or=6 pg/g ww) were comparatively low in all samples. Hepatic ethoxyresorufin O-deethylase (EROD) activity in some fish was elevated relative to reference rates at most sites, but was generally lower than previously reported activity in fish from heavily contaminated locations. The comparatively low PCB and TCDD-EQ concentrations together with elevated EROD activity may reflect exposure to polycyclic aromatic hydrocarbons. Reproductive biomarkers were consistent with chronic contaminant exposure at lower RGB sites; comparatively large percentages of intersex male largemouth bass, relatively low gonadosomatic indices, and elevated plasma vitellogenin concentrations in male fish were noted at three of the four stations. Large percentages of atretic eggs were also observed in the ovaries of female common carp from the Rio Grande at Brownsville, TX. Although many of the conditions noted may have other causes in addition to contaminant exposure, the biomarker results for the lower RGB sites are consistent with subtle responses of fish to contaminants, an interpretation supported by the chemical data of this and other investigations.

Animals↗
PubMed1999

[The effects of fish supplementation of platelet function, count and metabolism in healthy Japanese].

To investigate changes in platelet function, count and metabolism following fish intake among Japanese, we conducted an experimental intervention study of seven healthy Japanese volunteers (4 males and 3 females) aged 28-58 years. We supplemented their diets with an approximate daily intake of 200-400 g fish which is equivalent to about 10 g n3-polyunsaturated fatty acids (about 3.5 g eicosapentaenoic acid plus 5.0 g docosahexaenoic acid) during the 17 days. The study continued until the 23rd day after returning to an ad libitum diet. The proportion of serum n3-polyunsaturated fatty acids increased two-fold on 5th day and three-fold on 15th day of fish supplementation, but decreased to one and a half-fold on the 2nd day and returned to the level before fish supplementation on the 12th day after returning to an ad libitum diet. The proportion of serum n6-polyunsaturated fatty acids decreased by 17% to the level before fish supplementation on the 5th day, 33% on the 15th day of fish supplementation. However, the decrease was only 10% on the 2nd day and the proportion returned to the same level as before fish supplementation on the 12th day after returning to an ad libitum diet. As a result, the serum n3/n6 polyunsaturated fatty acid ratio increased four-fold on the 15th day of fish supplementation, and returned to the baseline level on the 12th day after returning to an ad libitum diet. Platelet counts decreased and the mean platelet volume increased during fish supplementation. Both parameters returned to the level before fish supplementation on the 12th day after returning to an ad libitum diet. The counts and proportion of large type platelets increased significantly during fish supplementation. Although platelet aggregation by ADP (adenosine 5'-diphosphate) did not change significantly, platelet aggregation by collagen tended to decrease during fish supplementation. Platelet factor 4, one of the indices of platelet activity, decreased significantly during fish supplementation. The mean serum triglyceride level declined during fish supplementation, but returned to the level just before fish supplementation on the 2nd day after returning to an ad libitum diet. The mean plasma fibrinogen level tended to decline during fish supplementation and remained lower until the 12th day after returning to an ad libitum diet. Habitual fish intake may attenuate the development of atherosclerosis and prevent ischemic heart disease through suppression of platelet activity, and by reducing platelet counts and serum triglyceride levels.

Adult↗
PubMed2003

[Evaluation of Antilles fish ciguatoxicity by mouse and chick bioassays].

Ciguatera is a common seafood poisoning in Western Atlantic and French West Indies. Ciguatera fish poisoning in the Caribbean is a public health problem. A toxicological study was carried out on 178 Caribbean fish specimens (26 species) captured off Guadeloupe and Saint Barthelemy between 1993 and 1999. The mouse bioassay and the chick feeding test were used to control fish edibility. Ciguatoxins presence was assumed when symptomatology was typical of ciguatera in mouse and chick. Fishes were classified in three groups: non toxic fish (edible), low toxic fish (not edible) and toxic fish (not edible). 75% of fishes were non toxic. Toxic fish specimens belonged to four families of high trophic level carnivores: Carangidae, Lutjanidae, Serranidae et Sphyraenidae. Percentages of toxic fishes to humans reached 55% for Caranx latus and 33% for Caranx bartholomaei and Caranx lugubris. Only a significant correlation between weight and toxicity was only found for C. latus and snappers. Small carnivorous groupers (Serranidae) were also toxic. Atoxic fish species were (a) pelagic fish (Coryphaena hippurus, Auxis thazard and Euthynnus pelamis), (b) invertebrates feeders (Malacanthus plumieri, Balistes vetula), (c) small high-risk fish or (d) fish of edible benthic fish families. Liver of four fishes (Mycteroperca venenosa, Caranx bartholomaei, Seriola rivoliana, Gymnothorax funebris) contained ciguatoxins at a significant level although their flesh was safe. This study confirms the usefulness of mouse and chick bioassays for sanitary control of fish.

Animals↗
PubMed1997

Scombroid fish poisoning: an overlooked marine food poisoning.

Scombroid fish poisoning is a food-borne chemical intoxication caused by certain spoiled fish that contain a large amount of histamine and some biogenic diamines. It has gradually become a world-wide medical problem and probably is the most common cause of fish poisoning. As the data on the incidents of scombroid fish poisoning in Taiwan remains scarce, we report 2 incidents of scombroid fish poisoning in Northern Taiwan. We collected data of the 2 outbreaks of suspected fish poisoning which were reported to us in 1996. An epidemiological investigation was undertaken. Questionnaire interviews were given to persons who ate lunch in the same cafeteria in outbreak 2. The leftover fish were sent for species identification and toxin analysis. The first incident involving 4 women occurred in March 1996. All cases experienced flush, dizziness, blurred vision and skin rashes after eating lunch. A non-scombroid fish of Makaira with histamine levels as high as 84.13 mg/100 g flesh was implicated in this incident. In August 1996, another incident involving some cases who ate lunch at the same cafeteria were investigated. A total of 146 questionnaires were distributed with a return of 132 questionnaires (90.4%). Fifty-five employees reported positive signs or symptoms; 48 persons who ate fish and 7 women who did not eat fish were ill. Fish was the only food associated with the illness with an attack rate of 73.8% (p < 0.001). The incriminated fish was later identified as a scombroid fish of Euthynnus with a histamine content of 271.9 mg/100 g flesh in 1 leftover piece and 118.5 mg/100 g flesh in another piece. Most cases in these 2 outbreaks received treatment with antihistamines and had rapid and complete recovery. The diagnosis of scombroid fish poisoning could be misdiagnosed as food allergy or bacterial food poisoning if physicians are not aware of such poisoning. The nonspecific but characteristic symptomatology of histamine food poisoning and previous consumption of fish should alert physicians to the possibility of scombroid fish poisoning. Unless complicated with shock or respiratory distress, supportive treatment with antihistamines usually concludes with a good prognosis. Toxin analysis of the fish flesh remains the most important step in approaching a confirmed diagnosis.

Adolescent↗
PubMed1993

Evaluation of the Hawaiian reef fishes with the solid phase immunobead assay.

This study presents data on the evaluation of a laboratory ciguatera kit based on the solid phase immunobead assay (SPIA) for the detection of ciguatoxin in Hawaiian reef fish. The SPIA was performed on fish catches by volunteer fishermen throughout the State of Hawaii. A total of 1,067 fish of various species were tested for ciguatoxin (CTX) using the SPIA kit. Of the total 1,067 fish tested, 510 were from Oahu, 402 from Hawaii, and 75 from Maui. The number of fish from Molokai, Kauai, and Lanai were 23, 20, and 7 respectively. Twenty percent of the total fish tested were positive, 41% borderline, and 39% negative for ciguatoxin. The highest percentage of SPIA- positive fish were from Hawaii (27%) followed by Oahu (19%) and Kauai (15%). These results correlate with the reported incidents from the Department of Health (DOH) of actual ciguatera poisoning in the State of Hawaii. Fish in all three categories of the SPIA test values were eaten. No false negatives were noted with individuals eating SPIA negative fish. Of the 232 SPIA borderline values eaten, 3 species of fish caused ciguatera poisoning. These fish included 2 papio, 1 mullet, and 1 po'ou. Of the 17 SPIA positive fish eaten, 5 caused ciguatera poisoning: 2 papio, a kole, an uhu, and a weke. The SPIA ciguatera test did protect the public when only SPIA-negative fish were eaten. The borderline and positive SPIA fish were generally unsafe, especially the positive fish. The data indicated that the probability of getting ciguatera with a SPIA positive fish was 1 out of 3.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗
PubMed2005

Heavy metals in commercial fish in New Jersey.

Levels of contaminants in fish are of particular interest because of the potential risk to humans who consume them. While attention has focused on self-caught fish, most of the fish eaten by the American public comes from commercial sources. We sampled 11 types of fish and shellfish obtained from supermarkets and specialty fish markets in New Jersey and analyzed them for arsenic, cadmium, chromium, lead, manganese, mercury, and selenium. We test the null hypothesis that metal levels do not vary among fish types, and we consider whether the levels of any metals could harm the fish themselves or their predators or pose a health risk for human consumers. There were significant interspecific differences for all metals, and no fish types had the highest levels of more than two metals. There were few significant correlations (Kendall tau) among metals for the three most numerous fish (yellowfin tuna, bluefish, and flounder), the correlations were generally low (below 0.40), and many correlations were negative. Only manganese and lead positively were correlated for tuna, bluefish, and flounder. The levels of most metals were below those known to cause adverse effects in the fish themselves. However, the levels of arsenic, lead, mercury, and selenium in some fish were in the range known to cause some sublethal effects in sensitive predatory birds and mammals and in some fish exceeded health-based standards. The greatest risk from different metals resided in different fish; the species of fish with the highest levels of a given metal sometimes exceeded the human health guidance or standards for that metal. Thus, the risk information given to the public (mainly about mercury) does not present a complete picture. The potential of harm from other metals suggests that people not only should eat smaller quantities of fish known to accumulate mercury but also should eat a diversity of fish to avoid consuming unhealthy quantities of other heavy metals. However, consumers should bear in mind that standards have a margin of safety.

Animals↗
PubMed2006

Mercury in fish available in supermarkets in Illinois: are there regional differences.

Media coverage has made the public aware of both the benefits and the risks from eating self-caught fish, but information on contaminants in commercial fish is much more limited, especially on a local level. The U.S. Food and Drug Administration website provides methylmercury data for a variety of fish, but for many species sample sizes are small and data are more than a decade old, whereas commercial fish sources are highly dynamic. A few state agencies are beginning to provide contaminant information for commercial fish, including canned tuna. We examined the mercury concentration of six types of fish purchased in supermarkets in Chicago, Illinois in 2005. We measured total mercury (methylmercury accounts for about 90% of the total mercury in fish). One key question was whether the concentrations of mercury in fish available locally were similar to those reported in other areas of the country and in the FDA U.S. national data base. Such information is critical for the public, especially pregnant women or those planning on pregnancy, making decisions about types and quantities of fish to consume. Some fish are available generally throughout the U.S., but others are more locally available, suggesting a need for site-specific information. This research was stakeholder driven, and reflected local interest in the safety of local fish. There were significant differences in mercury concentrations among the fish, ranging from a mean of 0.03 microg/g (ppm-wet weight) for salmon (Salmo spp.) to 1.41 ppm for swordfish (Xiphias gladius). Maximum values for three species of fish (orange roughy Hoplostethus atianticus, swordfish walleye Sander vitreus) were over 1 ppm (FDA action level), and all of the fish except salmon had some values above 0.5 ppm, the action level set by some states and countries. There were significant differences in mercury concentrations among three types of canned tuna (Thunnus spp): "gourmet tuna" had the least amount of mercury, and white tuna had the most. The mean concentrations reported in this study were generally similar to those reported by the FDA, but there were important differences: 1) although the mean mercury concentrations for orange roughy for the Chicago data was similar to the FDA data, the maximum concentration was higher; 2) the mean for the Chicago swordfish was higher than the FDA data (1.26 vs 0.97 ppm, methylmercury); 3) the maximum for tuna steaks was higher in the FDA data set; and, 4) mean values for grouper (Epinephelus spp.) were higher in the FDA data set than the Chicago data. Further, the FDA has virtually no data on walleye and none on "gourmet tuna". These conclusions suggest that there are enough variations between the local data (Chicago) and the FDA data to warrant periodic local monitoring of commercial fish to provide up-to-date information to consumers about mercury in the fish they eat.

Analysis of Variance↗
PubMed2003

Weighing health benefit and health risk information when consuming sport-caught fish.

Fish consumers may incur benefits and risks from eating fish. Health advisories issued by states, tribes, and other entities typically include advice about how to limit fish consumption or change other behaviors (e.g., fish cleaning or cooking) to reduce health risks from exposure to contaminants. Eating fish, however, may provide health benefits. Risk communicators and fish consumers have suggested the importance of including risk comparison information, as well as health risk-benefit comparisons in health advisory communications. To improve understanding about how anglers fishing in waters affected by health advisories may respond to such risk-risk or risk-benefit information, we surveyed Lake Ontario (NY, USA) anglers. We interviewed by telephone 4,750 anglers, 2,593 of which had fished Lake Ontario in the past 12 months and were sent a detailed mail questionnaire (1,245 responded). We posed questions varying the magnitude of health risks and health benefits to be gained by fish consumption, and varied the population affected by these risks and benefits (anglers, children, women of childbearing age, and unborn children). Respondents were influenced by health benefit and health risk information. When risks were high, most respondents would eat less fish regardless of the benefit level. When risks were low, the magnitude of change in fish consumption was related to level of benefit. Responses differed depending on the question wording order, that is, whether "risks" were posed before "benefits." For a given risk-benefit level, respondents would give different advice to women of childbearing age versus children, with more conservative advice (eat less fish) provided to women of childbearing age. Respondents appeared to be influenced more strongly by risk-risk comparisons (e.g., risks from other foods vs. risks from fish) than by risk-benefit comparisons (e.g., risks from fish vs. benefits from fish). Risk analysts and risk communicators should improve efforts to include risk-risk and risk-benefit comparisons in communication efforts, and to clarify to whom the health risks and benefits from fish consumption may accrue.

Adult↗
PubMed1994

[Mercury exposure by fish consumption in Rhine fishermen].

In this study 149 test persons were included, which were divided in 2 groups: consumption of Rhine fish (n = 77) and control group which consumed no Rhine fish (n = 72), but eventually fish from other sources. The consumption of Rhine fish averaged 1290 g per month (range: 100-5250 g per month), in the control group the consumption of fish averaged 340 g per month (range: 0-4000 g per month). The monthly fish consumption for inhabitants of Baden-Württemberg is in the range of 300 to 400 g. From this it can be seen that the control group consumed fish in the range of the general population, whereas in the group with Rhine fish consumption the quantity of consumed fish was 4 fold. In the group with Rhine fish consumption the levels of mercury in blood were in the geometric mean (GM) 2.41 micrograms/l, arithmetic mean (AM) 3.43 micrograms/l (range: 0.5-17.8 micrograms/l); control group an estimated GM: 0.68 micrograms/l, AM of 0.90 micrograms/l (range: 0.2-3.2 micrograms/l). The corresponding levels in hair were in the group with Rhine fish consumption GM: 1060 micrograms/kg, AM: 1410 micrograms/kg (range: 190-7200 micrograms/kg) and in the control group: GM 520 micrograms/kg, AM: 610 micrograms/kg (range: 190-2710 micrograms/kg). From this data it can be concluded that the consumption of Rhine fish gives rise to higher levels of mercury in blood (GM: 3.5, AM: 3.8 fold) and hair (GM: 2.0, AM: 2.3 fold). In the Umwelt-Survey of the German Bundesgesundheitsamt for the general German population an estimated GM of 0.46 microgram/l and AM of 0.74 microgram/l for mercury levels in blood was reported. The corresponding mercury concentrations determined in the group with Rhine fish consumption were 5.2. and 4.6 fold higher. No significant differences of mercury levels in urine were seen in the 2 groups (Rhine fish consumption GM: 0.57 microgram/l, AM: 0.84 microgram/l, range: < 0.1-4.7 micrograms/l; control group GM: 0.40 micrograms/l, AM: 0.93 microgram/l, range: < 0.1-13.6 micrograms/l). In both groups no correlation was found between mercury in urine and mercury in blood or hair respectively. For biological monitoring of organic mercury derived from fish consumption the determination of mercury in blood and hair is suited. The excretion of mercury in urine does not reveal an exposition with mercury from fish consumption.

Adult↗
PubMed1996

Effect of extreme fish consumption on dietary and plasma antioxidant levels and fatty acid composition.

OBJECTIVE: To assess the effects of high-fish and low-fish diets on plasma concentrations of fatty acids and selected antioxidants. DESIGN AND SUBJECTS: The effects of fish consumption on dietary and plasma antioxidant levels and fatty acid composition were studied as part of a large dietary survey of Finnish adults (n = 1861). High-fish consumers were matched with low-fish consumers and 41 pairs were identified. The members of each pair were of the same sex, from the same 10 y age group, and from the same or adjacent areas. There were 21 men and 20 women in each group, with a mean age of 54.3 y. METHODS: The fish consumption of the subjects was investigated with a qualitative food questionnaire. Additionally, a 3 d food record was used to estimate the diet. Two indices were defined to describe the oxidation potential of the diets. The plasma alpha-tocopherol, gamma-tocopherol, and beta-carotene concentrations and various fatty acids were analysed. RESULTS: The mean fish intake was 103 g/d in the high-fish and 5 g/d in the low-fish group. The dietary intakes of vitamin C, protein, total n-3 polyunsaturated fatty acids (PUFA), eicosapentaenoic acid, docosahexaenoic acid, mercury, selenium, and salt and the theoretical oxidative potential were higher (P < 0.05) and the saturated fatty acid intake lower (P < 0.01) in the high-fish than in the low-fish group. The dietary vitamin E intake was similar in both groups but the ratio of dietary vitamin E/PUFA was higher (P < 0.01) in the high-fish than in the low-fish group (0.85 and 0.75, respectively). The plasma n-3 PUFAs were higher (P < 0.001) and n-6 PUFAs lower (P < 0.001) in the high-fish than in the low-fish group. There were no differences in plasma antioxidant levels between the groups. CONCLUSION: This study shows that extreme fish consumption does not affect plasma antioxidant levels.

Adult↗
PubMed2001

Mercury contamination in freshwater, estuarine, and marine fishes in relation to small-scale gold mining in Suriname, South America.

The extent of mercury contamination in Surinamese food fishes due to small-scale gold mining was investigated by determination of the total mercury concentration in 318 freshwater fishes, 109 estuarine fishes, and 110 fishes from the Atlantic Ocean. High background levels were found in the piranha Serrasalmus rhombeus (0.35 microg Hg x g(-1) muscle tissue, wet mass basis) and the peacock cichlid Cichla ocellaris (0.39 microg x g(-1)) from the Central Suriname Nature Reserve. Average mercury levels in freshwater fishes were higher in piscivorous species than in nonpiscivorous species, both in potentially contaminated water bodies (0.71 and 0.19 microg x g(-1), respectively) and in the control site (0.25 and 0.04 microg x g(-1), respectively). Mercury concentrations in piscivorous freshwater fishes were significantly higher in rivers potentially affected by gold mining than in the control site. In 57% of 269 piscivorous freshwater fishes from potentially contaminated sites, mercury levels exceeded the maximum permissible concentration of 0.5 microg Hg x g(-1). The highest mercury concentrations (3.13 and 4.26 microg x g(-1)) were found in two piranhas S. rhombeus from the hydroelectric reservoir Lake Brokopondo. The high mercury levels in fishes from Lake Brokopondo were to some extent related to gold mining because fishes collected at eastern sites (i.e., close to the gold fields) showed significantly higher mercury concentrations than fishes from western localities. In the estuaries, mercury levels in ariid catfish (0.22 microg x g(-1)) and croakers (0.04-0.33 microg x g(-1)) were distinctly lower than those in piscivorous fishes from contaminated freshwater sites. In the isolated Bigi Pan Lagoon, the piscivores snook Centropomus undecimalis (0.04 microg x g(-1)) and tarpon Megalops atlanticus (0.03 microg x g(-1)) showed low mercury levels. Mercury levels were significantly higher in marine fishes than in estuarine fishes, even with the Bigi Pan fishes excluded. High mercury concentrations were found in the shark Mustelus higmani (0.71 microg x g(-1)), the crevalle jack Caranx hippos (1.17 microg x g(-1)), and the barracuda Sphyraena guachancho (0.39 microg x g(-1)), but also in nonpiscivorous species such as Calamus bajonado (0.54 microg x g(-1)), Haemulon plumieri (0.47 microg x g(-1)), and Isopisthus parvipinnis (0.48 microg x g(-1)). Mercury levels were positively correlated with the length of the fish in populations of the freshwater piscivores S. rhombeus, Hoplias malabaricus, and Plagioscion squamosissimus, in estuarine species (Arius couma, Cynoscion virescens, and Macrodon ancylodon), and in S. guachancho from the Atlantic Ocean.

Animals↗
PubMed2002

Consumption patterns and why people fish.

Recreational and subsistence fishing play major roles in the lives of many people, although their importance in urban areas is often underestimated. There are fish and shellfish consumption advisories in the New York-New Jersey harbor estuary, particularly in the waters of the Newark Bay Complex. This paper examines fishing behavior, consumption patterns, and the reasons that people fish in the Newark Bay Complex. I test the null hypotheses that there are no differences among Asians, Blacks, Hispanics, and Whites in consumption patterns for fish and crabs and in the reasons that they fish or crab. Most people either fished or crabbed, but not both. People who fish and crab ate more grams of crab than fish in a given meal; people who crab only consumed more grams of crab at a meal than those who fish only consumed of fish. Although 30% or more of the people who fished and crabbed in the Newark Bay Complex did not eat their self-caught fish or crabs 8-25% of the people ate more than 1500 g/month. Some people angling in the Newark Bay Complex are eating crabs at a rate well over 1500 g/month, and about 70% are eating crabs even though there is a total ban on both harvest and consumption because of the health risks from dioxin. Consumption patterns were negatively correlated with mean income and positively correlated with mean age. Most people rated relaxation and being outdoors the highest reasons for angling, although on an open-ended question they usually listed recreation. There were no ethnic differences in reasons for angling, although other studies have shown ethnic differences in consumption. Obtaining fish or crabs to eat, give away, trade, or sell were rated low, suggesting that consumption advisories fail partly because people are not primarily fishing for food.

Adult↗
PubMed2004

A randomized, double-blinded, placebo-controlled oral challenge study to evaluate the allergenicity of commercial, food-grade fish gelatin.

BACKGROUND: Recent interest in the labeling of foods and food proteins derived from allergenic sources necessitates determination of the potential allergenicity of such food ingredients. Fish gelatin is extracted from the skin of fish species known to elicit allergic reactions in sensitized individuals. OBJECTIVE: To determine the allergenicity of fish gelatin by double-blinded, placebo-controlled food challenges (DBPCFC) in clinically fish-allergic individuals. METHODS: Thirty fish-allergic patients diagnosed according to the EAACI Guidelines were included (age 9-50 years). Skin prick tests (SPT) and Histamine Release tests (HR) were performed with fish gelatin and codfish, and codfish-specific IgE was measured. All patients underwent DBPCFC with a cumulative dose of 14.61 g fish gelatin. RESULTS: In all 30 patients SPT, HR, and specific IgE to codfish were positive. SPT and HR with fish gelatin were positive in 3/30 and 7/30, respectively. One patient showed mild reaction to placebo and no reaction to the active challenge. Two patients reported mild subjective reactions to active challenge. Upon re-challenge one of them described subjective symptoms again to the active challenge (7.61 g cumulated dose of fish gelatin) with no reaction to placebo, while the other experienced very mild subjective symptoms to placebo and nothing to the active. The proportion of truly sensitive patients was estimated to 0.03 in the total study group. CONCLUSION: None of 30 fish allergic patients reacted adversely to the ingestion of 3.61 g cumulative dose of fish gelatin. In this study fish gelatin presents no risk to fish-allergic patients at the doses typically used. Statistically, these results indicate that there is 95% certainty that 90% of fish-allergic consumers will not react to ingestion of a 3.61 g cumulative dose of fish gelatin.

Adolescent↗
PubMed2005

Comparison of basal cytotoxicity data between mammalian and fish cell lines: a literature survey.

During the last 20 years, in vitro assays with fish cells have been used in ecotoxicology for testing chemicals, effluents and in toxicity identification evaluations (TIE) studies. Due to the good correlation found between the in vitro data and the in vivo fish data in ranking chemical toxicity, they have been proposed as an alternative to acute fish bioassays for toxicity screening of chemicals. Nevertheless, they are recognized to be less sensitive when compared with in vivo fish bioassays. Fish cells have slower cell cycles than mammalian cells, so it was suggested that mammalian cells could be more sensitive than fish cells for testing chemicals. However, as fish cells offer some advantages over mammalian cells, mainly related to their ease of handling, some authors found them preferable to use for routine testing. The present study was undertaken to analyze whether mammalian cell lines are more, less, or equally sensitive, compared to fish cells lines. To this end, basal cytotoxicity data from a literature survey of mammalian and fish cell lines have been compared. There was a good linear correlation of IC50 values (r = 0.915) between fish and mammalian cells for a set of 51 chemicals after 24-h of treatment. The correlation coefficient of IC50 values (r = 0.888) decreased when 24-h treated mammalian cells were correlated against 48-h treated fish cell lines. For the dataset selected for this study, fish and mammalian cells showed a similar sensitivity for most of the chemicals after being treated for 24 h. We conclude that fish and mammalian cells can equally well predict the basal toxicity of the set of chemicals used in this study, and that increased exposure periods did not increase the correlation between midpoint toxicities nor sensitivities for any of the cell lines used. The more practical handling of fish cells favors their recommendation as a better alternative for replacing fish bioassay than mammalian cells.

Animals↗
PubMed2002

Toxic contaminants and their biological effects in coastal waters of Xiamen, China. I. Organic pollutants in mussel and fish tissues.

Organochlorines and organophosphates were measured in four fish species (Lateolabrax japonicus, Pagrasomus major, Miichthys miiuy and Epinephalus awoara) and the mussel Perna viridis collected from aquaculture cages in coastal waters of Xiamen, China. Polycyclic aromatic hydrocarbon (PAH) metabolites were also measured in fish bile. Sites in Xiamen coastal waters (the harbour, Maluan and Tongan) are compared with a "cleaner" reference site at Dongshan Island. DDT was found in livers of all fish sampled (May 1998, 1999 and December 1999) ranging from 0.15 to 2.2 microg/g WW, but levels in muscle tissue (<0.5 ng/g to 0.22 microg/g WW) were at least an order of magnitude lower in the harbour, and were not detectable (<0.5 ng/g) in Tongan samples. All other pesticides examined were not detected in fish or mussels, except for dieldrin in one liver sample (0.07 microg/g WW). Food of the caged fish, small fish and dried pellets, had very low (0.015-0.027 microg/g WW) or non-detectable levels of DDT, indicating significant bioaccumulation of contaminants in caged fish and/or other possible sources of uptake (water and sediments). DDT levels in fish varied with species. DDT contamination in fish livers and whole mussels varied significantly with location. Highest concentrations in fish occurred in the harbour, and less consistently so in Tongan. Dongshan and Maluan had comparatively low levels of DDT. Relatively low residues of DDT in both fish and mussels at Dongshan likely reflect lower levels of pesticide input at this reference site. However, the low levels of DDT contamination in fish tissues from Maluan were unexpected in view of the close proximity of the harbour and possibly reflect the removal of particulate-bound contaminants by the intensive bivalve culture there. Consistently high proportions of DDT in the form of the parent compound (p,p'-DDT: fish 30-45%; mussels 40-65%) from all sites suggest recent releases of this chemical to the environment. Levels of two main groups of PAH metabolites (naphthalene and phenanthrene) in fish bile suggest a different environmental distribution pattern than that of pesticides, in that Dongshan fish appear to be no less exposed to hydrocarbons than those from Xiamen coastal waters.

Animals↗
PubMed1990

An emerging role for a cardiac peptide hormone in fish osmoregulation.

It is clear from the extant literature that various fish groups face chronic osmoregulatory problems that depend on the surrounding salinity. Their physiologic and hormonal responses are largely those seen in the mammals, but their terrestrial descendants have lost osmoregulatory structures such as gills and rectal glands and depend primarily on renal function. A data base is now emerging that strongly suggests that a putative atriopeptin plays a role in osmoregulation in fishes. This conclusion is supported by the fact that heterologous AP produces relevant physiologic responses (e.g. natriuresis, vasodilation, stimulation, or inhibition of Na+ secretion by intestine, gills, and rectal gland) in both teleosts and elasmobranchs. Moreover, cardiac and brain extracts from fish can produce similar effects in both fishes and mammals, and these tissues from various fish groups contain immunoreactive AP, as does plasma. Both physiologic and immunologic evidence suggests that the ventricle may be a significant source of AP in fishes, contrary to the situation in mammals. Finally, osmotic perturbations result in a change in plasma and tissue APir levels. The finding that plasma APir levels increase in sea water, and that heterologous AP stimulates salt secretion by the teleost gill and shark rectal gland, and inhibits salt uptake by the teleost intestine, suggests that AP may primarily play a role in salt, rather than fluid, secretion in fishes. The fact that in mammals AP inhibits prolactin secretion, but is itself stimulated by cortisol, supports this conclusion, since prolactin is generally considered to be the dominant osmoregulatory hormone in freshwater fishes, and cortisol serves this function in marine fishes. In addition, if AP inhibits brain AVT release in fishes, as it apparently inhibits vasopressin release in mammals, this also would be adaptive in marine fishes since AVT in fishes is diuretic, rather than antidiuretic. Interactions between AP and these hormones (prolactin, cortisol, and ATV) have not been studied in fishes to date, but these theoretical interactions do lend support to the hypothesis that AP may function primarily in salt homeostasis in fishes. At least one potential hormonal interaction counters this argument, however. Atriopeptin is known to inhibit the production and effects of angiotensin II in mammals, and since this hormone is apparently dipsogenic in fishes, it may play a critical role in osmoregulation in sea water. Finally, it is of some historical interest that in Keys' (67) original description of the eel heart-gill perfusion system in 1931 he commented that gill resistance remained constant for hours only if the heart itself was perfused.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗