除虫脲在棉叶和土壤中消解动态分析及棉子中残留量膳食摄入评估

目的评价除虫脲在棉叶、土壤中的消解趋势和土壤及棉子中的残留水平。方法棉叶、土壤样品经乙腈提取、氯化钠盐析、弗罗里硅土固相萃取柱净化后,采用高效液相色谱-光电二极管阵列检测器检测;同时对2014年和2015年除虫脲在河南和北京两地棉叶及土壤中的残留消解动态进行分析并对棉子中的最终残留量进行膳食摄入评估。结果除虫脲在棉子、棉叶和土壤空白样品添加的平均回收率在79%~103%之间,相对标准偏差在3%~15%之间,最低检测浓度均为0.1 mg/kg。棉叶中除虫脲的残留消解半衰期在5.0~8.6 d之间,土壤中残留消解半衰期在3.8~14 d之间。按本试验方式进行施药及采样后,棉子中除虫脲的最终残留量低于0.1 mg/kg,土壤中的残留量低于0.19 mg/kg。结论除虫脲普通人群的国家估计每日摄入量是0.873229mg/kg·bw,占日允许摄入量的69.3%左右,认为对一般人群健康不会产生不可接受的风险。     

Examination of isomer specific bioaccumulation parameters and potential in vivo hepatic metabolites of syn- and anti-Dechlorane Plus isomers in juvenile rainbow trout (Oncorhynchus mykiss)

Juvenile rainbow trout (Oncorhynchus mykiss) were exposed in the laboratory to elevated doses of syn- and anti-isomers of Dechlorane Plus (DP) via their diet for 49 days (uptake phase), followed by 112 days of untreated food (depuration phase) to examine bioaccumulation parameters and possible metabolic products. Three groups of 60 fish were used in the study. Two groups were exposed separately to food fortified with known concentrations of syn- (0.79 +/- 0.03 microg/g, lipid weight) and anti-DP (1.17 +/- 0.12 microg/g, lipid weight) while a third control group was fed unfortified food. Neither isomer reached steady-state after 49 days of exposure. Only the syn-isomer accumulated linearly in the fish (whole-body minus liver) during the dosing phase with a calculated uptake rate constant of 0.045 +/- 0.005 (arithmetic mean +/- 1 x standard error) nmoles per day. A similar uptake rate was also observed for this isomer in the liver. The elimination of both isomers from the whole fish (minus liver) obeyed first order depuration kinetics (syn-: r2 = 0.6427, p < 0.001, anti-: r2 = 0.5350, p < 0.005) with calculated half-lives (t1/2) of 53.3 +/- 13.1 (syn-) and 30.4 +/- 5.7 (anti-) days. Elimination of the isomers from the liver was difficult to interpret because of suspected enterohepatic circulation and redistribution of the isomers in the liver during clearance from other tissues. The biomagnification factor (BMF, determined in whole fish minus liver) of the syn-isomer (5.2) was greater than the anti-isomer (1.9) suggesting that the former isomer is more bioavailable. A suite of metabolites were screened for in the liver including dechlorinated, hydroxylated, methoxylated and methyl sulfone degradates. Even with the purposely high dose used in the uptake phase, none of these degradates could be detected in the extracts. This suggests that if metabolites of DP are detected in fish from aquatic food webs their presence is likely not from in vivo biotransformation of the parent compound.     

Tissue distribution and depuration kinetics of waterborne 14C-labeled light PAHs in mummichog (Fundulus heteroclitus)

Light polycyclic aromatic hydrocarbons (PAHs) of petrogenic origin are commonly found in estuaries and coastal areas. Though they are known to be toxic to fish, little is known about their uptake and tissue distribution. This paper reports on the results of a study on uptake, elimination, and tissue distribution of three waterborne 14C-labeled PAHs in the mummichog, Fundulus heteroclitus, using whole-body autoradiography. After a 24 h exposure to 1 μCi·L(-1) of 14C-naphthalene, 14C-1-naphthol, and 14C-phenanthrene, fish were transferred to clean water and tissue distribution examined after 0, 1, 3, 7, 14, and 21 days of depuration. All compounds were readily accumulated by fish and were also rapidly eliminated (t0.5 range=1.1 to 3.0 days). Most of the radioactivity in naphthalene- and phenanthrene-treated fish was found in gall bladder?liver>intestinal lumen. In naphthol-exposed fish, an important labeling of some brain areas was observed. Brain of naphthalene-exposed fish was also labeled after 24 h depuration, indicating that exposure to naphthalene may result in metabolite accumulation in the brain. This is the first study showing that naphthalene, naphthol, and/or unidentified metabolite(s) can accumulate in brain tissues, which may impair normal brain function.     

Uptake, elimination, and relative distribution of perchlorate in various tissues of channel catfish

This study was undertaken to determine the kinetics of uptake and elimination of perchlorate in channel catfish, Ictalurus punctatus. Perchlorate--an oxidizer used in solid fuel rockets, fireworks, and illuminating munitions--has been shown to effect thyroid function, causing hormone disruption and potential perturbations of metabolic activities. For the uptake study, catfish were exposed to 100 mg/L sodium perchlorate for 12 h to 5 d in the laboratory. Perchlorate in tissues was analyzed using ion chromatography. The highest perchlorate concentrations were found in the head and fillet, indicating that these tissues are the most important tissues to analyze when determining perchlorate uptake into large fish. To calculate uptake and elimination rate constants for fillet, gills, G-I tract, liver, and head, fish were exposed to 100 ppm sodium perchlorate for 5 days, and allowed to depurate in clean water for up to 20 days. The animals rapidly eliminated the perchlorate accumulated showing the highest elimination in fillet (Ke = 1.67 day(-1)) and lowest elimination in liver (Ke = 0.79 day(-1)).     

Comparative effects of dietary methylmercury on gene expression in liver, skeletal muscle, and brain of the zebrafish (Danio rerio)

Effects of dietary methylmercury (MeHg) on gene expression were examined in three organs (liver, skeletal muscle, and brain) of the zebrafish (Danio rerio). Adult male fish were fed over 7, 21, and 63 days on three different diets: one control diet (C0: 0.08 microg of Hg g(-1), dry wt) and two diets (C1 and C2) contaminated by MeHg at 5 and 13.5 microg of Hg g(-1), dry wt. Total Hg and MeHg concentrations were determined in the three organs after each exposure duration, and a demethylation process was evidenced only in the liver. Thirteen genes known to be involved in antioxidant defenses, metal chelation, active efflux of organic compounds, mitochondrial metabolism, DNA repair, and apoptosis were investigated by quantitative real-time RT-PCR and normalized according to actin gene expression. Surprisingly, no change in the expression levels of these genes was observed in contaminated brain samples, although this organ accumulated the highest mercury concentration (63.5 +/- 4.4 microg g(-1), dry wt after 63 days). This lack of genetic response could explain the high neurotoxicity of MeHg. coxI and cytoplasmic and mitochondrial sod gene expressions were induced early in skeletal muscle and later in liver, indicating an impact on the mitochondrial metabolism and production of reactive oxygen species. Results demonstrated that skeletal muscle was not only an important storage reservoir but was also affected by MeHg contamination. The expression of the metallothionein mt2 and the DNA repair rad51 genes was up-regulated in liver between 21 and 63 days, whereas in skeletal muscle, mt2 remained uninduced, and gadd and rad51 were found to be repressed.     

Effect of an insecticide controlled-release bolus on a milk antibiotic residue test

Following the use of diflubenzuron controlled-release insecticide boluses in a dairy herd, there was a concern that post-calving cows were testing positive on a milk antibiotic residue test for more milkings than they had prior to the use of diflubenzuron. A field trial was conducted to examine for possible effects of diflubenzuron milk residues on the milk antibiotic residue test, Delvotest-P. Data of 24 cows in the treatment group and 29 cows in the control group were analyzed. There was no significant difference in the number of milkings after calving in which the milk tested positive on the milk antibiotic residue test between the treatment (2.75 +/- .94) and control (2.97 +/- 1.05) groups when cows in all lactations were analyzed or when analyzed by lactation (1, 2, and greater than or equal to 3). It was concluded that the use of diflubenzuron boluses had no effect on the milk antibiotic residue test.     

Dietary exposure of juvenile rainbow trout (Oncorhynchus mykiss) to 1,2-bis(2,4,6-tribromophenoxy)ethane: bioaccumulation parameters, biochemical effects, and metabolism

Juvenile rainbow trout (Oncorhynchus mykiss) were exposed in the laboratory to an environmentally relevant dose of 1,2-bis(2,4,6-tribromophenoxy)ethane (BTBPE) via their diet for 49 days, followed by 154 days of untreated food to examine bioaccumulation parameters, potential biochemical effects, and metabolic products. There was a linear increase in the amount of BTBPE in fish during the uptake phase of the experiment, and an uptake rate constant of 0.0069 +/- 0.0012 (arithmetic mean +/- 1 x standard error) nmoles per day was calculated. The elimination of BTBPE from the fish obeyed first-order depuration kinetics (r2 = 0.6427, p < 0.001) with a calculated half-life of 54.1 +/- 8.5 days. The derived biomagnification factor of 2.3 +/- 0.9 suggests that this chemical has a high potential for biomagnification in aquatic food webs. Debrominated and hydroxylated metabolites were not detected in liver extracts and suggest that either biotransformation or storage of BTBPE-metabolites in the hepatic system of fish is minor or that our exposure time frame was too short. Similar concentrations of circulating thyroid hormones, liver deiodinase enzyme activity, and thyroid glandular histology suggest that BTBPE is not a potent thyroid axis disruptor.     

黄瓜汁鱼丸的研制及冷藏过程中品质变化规律的研究

通过3因素3水平的正交实验,优化了黄瓜汁、鸡蛋清、淀粉的添加量对鱼丸质构特性及感官品质的影响,并研究了其在冷藏条件下的品质变化规律。结果显示,在最佳配料比为:黄瓜汁17%、鸡蛋清16%、淀粉21%的条件下,真空包装的黄瓜汁鱼丸在冷藏过程中随着贮藏时间的延长,3d以后pH出现一定程度的下降,白度呈不规律变化,细菌总数、硬度显著增加,其中弹性和硬度呈良好的负相关;核磁共振分析结果显示,黄瓜汁鱼丸具有4种流动性不同的水分,其对应的弛豫时间分别为T21、T22、T23,T24(0ms相似文献   

Speciation of hepatic Zn in trout exposed to elevated waterborne Zn using X-ray absorption spectroscopy

The long-term impacts of chronic metal exposure for aquatic biota are not well understood, partly due to a lack of understanding of metal speciation within tissues. The objective of this study was to determine hepatic Zn speciation of rainbow trout (Oncorhnychus mykiss) exposed to Zn-enriched water in relation to unexposed (control) fish,through direct analysis of freeze-dried liver samples using synchrotron X-ray absorption spectroscopy (XAS). Juvenile rainbow trout (n=30) were exposed to Zn in a two-step process, 200 microg L(-1) for 14 days, followed by 370 microg L(-1) for 23 days. Thirty other trout were grown in a control treatment (10 microg Zn L(-1)). At the end of the experiment, three liver samples per treatment were collected, freeze-dried, ground, and mixed homogeneously. Although Zn concentration was higher in the Zn-exposed livers than in the control livers (22.32 vs 13.73 mg kg(-1), respectively; p < 0.05), Zn speciation was similar for both groups. Extended X-ray absorption fine structure (EXAFS) spectroscopy indicated that Zn was coordinated to 4 sulfur atoms with an average Zn-S bond distance of 2.31 +/- 0.02 A. Sulfur K-XANES analysis confirmed that S was predominantly in reduced organic form analogous to cysteine. Our results are consistent with previous evidence for Zn(II) bonding to S in metallothionein proteins. These results suggest that the mechanisms for dealing with the extra load of bioaccumulated Zn in high exposure conditions were the same as in the control group.     

Cytochrome P450 1A expression in midwater fishes: potential effects of chemical contaminants in remote oceanic zones

Cytochrome P450 1A (CYP1A) induction is a robust marker for exposure to polynuclear aromatic hydrocarbons and planar halogenated aromatic hydrocarbons that are aryl hydrocarbon receptor agonists. We examined CYP1A expression in mesopelagic fishes from the western North Atlantic. Individuals in 22 species were obtained from slope water and the Sargasso Sea in 1977, 1978, and 1993. Aryl hydrocarbon hydroxylase (AHH), a CYP1A activity, was detected in liver from all species in 1977/78. In some, including Gonostoma elongatum, AHH was inhibited by the CYP1A inhibitor alpha-naphthoflavone. CYP1A-dependent ethoxyresorufin O-deethylase (EROD) was detected in liver microsomes of all species in 1993; rates were highest in G. elongatum and Argyropelecus aculeatus. Immunoblot analysis with the CYP1A-specific monoclonal antibody 1-12-3 detected a single microsomal protein band in most 1993 samples; the highest content was in G. elongatum. Immunohistochemical analysis showed CYP1A staining in gill, heart, kidney, and/or liver of several species. Extracts of the 1993 G. elongatum and A. aculeatus, when applied to fish hepatoma cells (PLHC-1) in culture, elicited a significant induction of EROD in those cells. The capacity of the extracts to induce CYP1A correlated with the content of PCBs measured in the same fish (2-4.6 ng/g total body weight). Mesopelagic fish in the western North Atlantic, which experience no direct exposure to surface waters or sediments, are exposed chronically to inducers of CYP1A at levels that appear to be biochemically active in those fish.     

Transfer profile of orally and intramuscularly administered tetrodotoxin to artificial hybrid specimens of the pufferfish Takifugu rubripes and Takifugu porphyreus

Tetrodotoxin (TTX) was administered to artificially hybridized specimens of the pufferfish Takifugu rubripes and Takifugu porphyreus to investigate toxin accumulation in hybrids and TTX transfer/accumulation profiles in the pufferfish body. In test fish administered TTX-containing feed homogenate at a dose of ～400 MU/fish by oral gavage using a syringe (OGA group), the toxin content (MU/g tissue) of the digestive tract rapidly decreased and that of the liver increased from 1 to 24 h after administration. From 24 to 120 h, the toxin content of the liver decreased gradually, and the toxin appeared in the skin. On the other hand, intramuscularly administered TTX (400 MU/fish) was rapidly transferred to the liver and skin via the blood, and only a little toxin remained in the muscle even at 1 h (IMA group). The total amount of toxin remaining in the whole body (% of administered toxin) was 31-45% in the OGA group, and 42-74% in the IMA group; the scores in the OGA group were generally lower than those in the IMA group. In both OGA and IMA groups, the greatest amount of toxin accumulated in the liver (23-52%) after 8 h, followed by the skin (11-21%) after 72 h. The TTX administration experiment, especially using the oral gavage administration method, revealed that skins and livers of 'torama' pufferfish hybrid are endowed with TTX-accumulating ability, but the muscles are not, and that TTX taken up from toxic feed to the pufferfish body is transferred first to the liver and then to the skin via the blood.     

Monitoring perfluorinated surfactants in biota and surface water samples following an accidental release of fire-fighting foam into Etobicoke Creek

Perfluorinated surfactants have emerged as priority environmental contaminants due to recent reports of their detection in environmental and biological matrices as well as concerns regarding their persistence and toxicity. In June 2000, 22000 L of fire retardant foam containing perfluorinated surfactants was accidentally released at L. B. Pearson International Airport, Toronto, ON, and subsequently entered into Etobicoke Creek, a tributary to Lake Ontario. A suite of analytical tools that include liquid chromatography/tandem mass spectrometry (LC/MS/MS) and 19F NMR were employed to characterize fish (common shiner, Notropus cornutus) and surface water samples collected following the discharge of the perfluorinated material. Total perfluoroalkanesulfonate (4, 6, and 8 carbons) concentrations in fish liver samples ranged from 2.00 to 72.9 microg/g, and total perfluorocarboxylate (5-14 carbons) concentrations ranged from 0.07 to 1.02 microg/g. In addition to fish samples, total perfluoroalkanesulfonate (6 and 8 carbons) concentrations were detected in creek water samples by LC/MS/MS over a 153 day sampling period with concentrations ranging from <0.017 to 2260 microg/L; perfluorooctanoate concentrations (<0.009-11.3 microg/L) were lower than those observed for the perfluoroalkane-sulfonates. By 19F NMR, the total perfluorinated surfactant concentrations in surface water samples ranged from < 10 to 17000 microg/L. A bioaccumulation factor range of 6300-125000 was calculated for perfluorooctanesulfonate, based on concentrations in fish liver and surface water. The residence time of perfluorooctanesulfonate in Etobicoke Creek as well as the high bioaccumulation in fish liver suggests that perfluorinated surfactants will persist and bioaccumulate following release into the aquatic environment.     

Evaluation of insecticide dips as protectants of stored dried fish from dermestid beetle infestation

Dried Tilapia species were dipped for 4 s in 10 l. of solutions containing, at two concentrations, pirimiphos-methyl, iodofenphos, fenitrothion, diflubenzuron or deltamethrin. After draining excess fluid, the fish were left in a store at Lake Turkana, Northern Kenya, where they were subjected to infestation by Dermestes maculatus Degeer (Coleoptera: Dermestidae). The treatments were compared with untreated or water dipped controls and to fish dipped in a commercial formulation of pyrethrins synergised with piperonyl butoxide. All treatments gave good protection for 2 months but only the deltamethrin gave adequate control for 6 months. Deltamethrin had a distinct repellent effect which was lacking with other treatments except the natural pyrethrins. There was no difference in effectiveness between high and low dosages nor between different formulations. Low dosages of each treatment produced residues in fish that were similar to the maximum recommended for raw cereals and pulses and can be regarded as levels that would be safe for human consumption. The results suggest that deltamethrin and pirimiphos-methyl have potential for use as long lasting protectants of dried fish in store.     

EXTENDING THE SHELF LIFE OF SET FISH BALL

Set fish ball is an extruded surimi‐based product that is popular in Singapore and other Southeast Asian countries. Oversetting of set fish ball occurs at chilled temperature during storage. Shelf‐life extension of set fish ball by reducing oversetting conditions and microbial counts were examined. Encapsulated citric acid (CT) and glucono‐delta‐lactone (GDL) were used to reduce oversetting. Acetic acid, GDL and chitosan were used to inhibit the growth of microorganisms. Shelf life was measured for a period of 21 days at 4C. At day 21, a reduction of 46, 56 and 26% in breaking force compared with the control (without additives) was observed for 0.5% GDL, 1.0% GDL and CT, respectively. GDL at 1.0% was shown to be the most effective in controlling the oversetting of set gel. Chitosan (1%) dissolved in acetic acid maintained both aerobic plate and yeast counts at <1 log cfu/g throughout 21 days of storage.     

Oxytetracycline residues in rainbow trout analysed by a rapid HPLC method

A rapid and sensitive HPLC method was developed for the determination of oxytetracycline in fish tissues (muscle and liver) based on a clean-up and concentration procedure on Sep-Pak C18. At a coastal fishfarm rainbow trout (Salmo gairdneri) suffering from Vibrio anguillarum were treated with 75 mg oxytetracycline per kg fish and day for ten days. Oxytetracycline residues above the limit of determination (0.005 micrograms/g) were found in fish 82 days after treatment. The recoveries from spiked tissues were about 60% and 70% for muscle and liver, respectively.     

Tissue distribution and residue depletion of metronidazole in rainbow trout (Oncorhynchus mykiss)

Tissue distribution and residue depletion of metronidazole (MNZ) was studied in rainbow trout (Oncorhynchus mykiss) following oral administration of MNZ in feed at the average dose of 25 mg kg^?1 body weight day^?1 for 7 days at 11 ± 2°C. The MNZ concentration in feed was 0.25% while daily feed intake was 1% of body weight. The concentrations of MNZ and its main metabolite, hydroxymetronidazole (MNZOH), in fish tissues were determined by LC-MS/MS. The drug was well distributed in tissues with maximum concentrations on day 1 post-administration. At this time, the mean MNZ concentrations in muscle, skin, kidney, liver and gill were 14 999, 20 269, 15 070, 10 102 and 16 467 µg kg^?1 respectively. MNZ was converted into MNZOH with the ratio of MNZOH:MNZ up to 7% in all fish tissues throughout the withdrawal period. This shows that MNZ itself is the main residue in rainbow trout. MNZ was detected at the level close to the decision limit (0.20 µg kg^?1) in muscle, skin and muscle with adhering skin up to 42 days, while in kidney, liver and gill it was up to 28 days post-administration. MNZOH was eliminated more rapidly from fish tissues and it was present in muscle alone up to 21 days. The elimination half-lives of MNZ and MNZOH in rainbow trout tissues were 1.83–2.53 and 1.24–2.12 days, respectively. When muscle without skin was analysed, higher MNZ and MNZOH concentrations were detected, and for a longer period of time, than in muscle with adhering skin. Thus muscle alone could be more appropriate for the effective residue control of MNZ in rainbow trout. For the same reason, it is also essential to ensure direct cooling immediately after sampling, since MNZ and its metabolite degrade in fish muscle and skin stored in non-freezing conditions.     

ATPase and Lactate Dehydrogenase Activities in Frozen Stored Fish Muscle as Indices of Cold Storage Deterioration

The effect of prolonged cold storage on muscle adenosine triphosphatase (ATPase) and lactate dehydrogenase (LDH) activities was studied in a variety of fresh water and brackish water fish. Decrease in enzyme activity was observed in all samples stored frozen (- 20°C) over a period of 180 days. Highly significant negative correlation was observed between enzyme activity and frozen storage period with mullet, pearlspot, milk fish and tilapia. Significant linear correlations were observed between decrease in enzyme activities and other biochemical indices and sensory scores. The results indicated that loss of activities of ATPase and LDH in fish muscle was significantly related to early changes in quality of frozen stored fish.     

Tissue distribution and depuration of 4-tert-octylphenol residues in the cyprinid fish,Scardinius erythrophthalmus

Alkylphenols are present in the aquatic environment through the degradation of alkylphenolpolyethoxylate surfactants in sewage treatment works. Branched chain 4-alkylphenols have been shown to retard testicular growth and stimulate vitellogenin synthesis in freshwater fish. We conducted in vivo studies in order to determine the fate and persistence of radiolabeled 4-tert-octylphenol (tOP) in the cyprinid fish, rudd (Scardinius erythrophthalmus). Sexually mature rudd were exposed to a concentration of 4.7 microg/L of [14C] tOP in a flow through system for 10 days. Radioactive residues were extracted from soft tissues and analyzed by radio-high-performance liquid chromatography. tOP accumulated as the major residue in muscle, ovary, and testis with bioconcentration factors of 24, 85, and 169, respectively. tOP residues in blood, gill, kidney, liver, and bile were extensively metabolized. Analysis of tOP residues in bile revealed 10 major metabolites, which were identified by GC-MS as products of aromatic and aliphatic hydroxylation, glucuronidation, and glucosidation. Depuration studies with exposed fish placed in clean water for up to 10 days resulted in a rapid loss of soluble residues from the tissues with half-lives of between 0.7 and 1.0 days (muscle, testis, ovary, gill, blood, kidney), 1.7 days (liver), and 5.9 days (bile). A further portion of radioactive residues was extracted from blood, gill, kidney, and liver after alkaline digestion, suggesting the formation of covalently bound protein adducts in these tissues. This study suggests that although para-alkyphenolic xenoestrogens can accumulate in muscle and the gonads of adult fish, residues are rapidly depurated from these tissues. Furthermore, analysis of the parent alkylphenol in bile, after hydrolysis of the conjugates, is likely to significantly underestimate the total concentration of alkylphenol residues and may not serve as an appropriate biomarker for quantifying the exposure of wild fish to alkylphenols.     

Long-term environmental fate of perfluorinated compounds after accidental release at Toronto airport

Perfluorooctane sulfonate (PFOS; a perfluorinated compound or PFC), its salts, and perfluorooctane sulfonyl fluoride have recently been listed in Annex B of the Stockholm Convention due to their widespread presence, persistence, and toxicity. Because of the persistent nature of PFCs, it is generally presumed that the impact of direct discharges of these chemicals on a receiving environment would be long-lasting. However, long-term environmental fate studies based on field measurements are rare. We examined spatial and long-term (9 year) temporal trends of PFCs in water, sediment, fish, and fish liver collected in 2003, 2006, and 2009 from 10 locations spanning ～20 km in Etobicoke and Spring Creeks, where an accidental release of fire fighting foam containing PFOS from nearby Toronto International Airport occurred in 2000. Even a decade after the spill, sediment PFOS concentrations are still elevated in Spring Creek Pond which received the foam discharge; however, the major impact is relatively localized likely due to the stormwater management nature of the pond and the diluting effect of Etobicoke Creek. Fish and fish liver PFOS concentrations at a Spring Creek location downstream of Spring Creek Pond declined by about 70 and 85%, respectively, between 2003 and 2009. PFOS in water at locations further downstream in Etobicoke Creek have declined by >99.99% since the spill; however, the 2009 water and fish levels were ～2-10 times higher than upstream locations likely due to the long-term impact of the spill as well as urbanization. The decrease in the upstream PFOS concentrations likely reflects the reduction of PFOS sources due to phased out production by 3M and regulations on the use of PFOS in fire fighting foams. Field-based sediment/water distribution coefficients (K(D)) and bioaccumulation factors (BAF) were calculated from environmental measurements. Log K(D) values were 0.54-1.65 for perfluoroalkyl sulfonates (PFASs) and 1.00-1.85 for perfluorocarboxylates (PFCAs). Log BAF(fish) ranged from 1.85 to 3.24 for PFASs and 0.88-3.47 for PFCAs, whereas log BAF(fish liver) ranged from 2.1-4.3 for PFASs and 1.0-5.0 for PFCAs.