A Weight of Evidence Approach to the Aquatic Hazard Assessment of Bisphenoi A

Bisphenol A (BPA; 4,4-isopropylidene diphenol) is a chemical intermediate used primarily in the production of epoxy resins and polycarbonate products. BPA has been identified in surface waters and, hence, has been the subject of considerable research into its potential effects on aquatic organisms. Available literature on the aquatic toxicity of BPA was reviewed for quality against European Union TGD and Organization of Economic Cooperation and Development GLP principles. From this review, studies of suitable quality covering numerous ecologically relevant endpoints were identified to evaluate the survival, growth, and reproductive success of aquatic organisms exposed to BPA. Those studies yielded approximately 70 no observed effect concentrations (ranging from 16 to 3640 μg/L) and lowest observed effect concentrations (160 to 11,000 μg/L) that were considered in this weight of evidence assessment. Across all data, adverse effects on survival, growth, and reproduction occurred only at concentrations of 160 μg/L and above. Secondary biochemical (e.g., vitellogenin induction) and morphological (e.g., gonad histology) data provide insight into mechanisms of action, but do not correlate with apical endpoints related to survival, growth, and reproduction. Comparing the weight of the evidence of the aquatic toxicity data that showed chronic effects at 160 μg/L and higher with typical surface water concentrations in the range of 0.001 to 0.10 μg/ L, BPA is unlikely to cause adverse effects on aquatic populations or ecosystems.     

Relationships between Aquatic Hazard Quotients and Probabilistic Risk Estimates: What Is the Significance of a Hazard Quotient >1?

This study examined relationships between hazard quotients (HQ) and probabilistic estimates of aquatic ecological risk. Questions addressed included the magnitude at which an HQ equates to significant risk, and the factors influencing the HQ-risk relationship. The analysis was based upon predicted exposure concentrations (PEC) for copper, hypothetical predicted no effect concentrations (PNEC) distributions, and measured PNEC data for aquatic species acutely and chronically exposed to copper, ammonia, cadmium, cyanide, dieldrin, DDT, phenanthrene, silver. and zinc. The cumulative PNEC and PEC distributions differed in slopes and magnitudes. The relationship between HQ and probabilistic risk, both of which were computed using conventional techniques, depended on the slopes of the PNEC and PEC distributions. Hazard quotients equaling 1.0 affected ～ 5% of the species because they were based on PNECs intended to protect 5% of the species. Hazard quotients greater than 1.0 depended on PNEC slope. For example, HQs for toxicants with the steeper PNEC distributions affected a large percentage of species (18 to 49%, depending on slope) at HQ=2 to 3. Other factors (e.g., variability in both PEC and PNEC data, and use of arithmetic or geometric means or their confidence limits) had variable influences on the HQ-risk relationship.     

Evaluation of Ecotoxicity Effect Indicators for Use in LCIA (10+4 pp)

Goal, Scope and Background The paper describes different ecotoxicity effect indicator methods/approaches. The approaches cover three main groups, viz. PNEC approaches, PAF approaches and damage approaches. Ecotoxicity effect indicators used in life cycle impact assessment (LCIA) are typically modelled to the level of impact, indicating the potential impact on 'ecosystem health'. The few existing indicators, which are modelled all the way to damage, are poorly developed, and even though relevant alternatives from risk assessment exist (e.g. recovery time and mean extinction time), these are unfortunately at a very early stage of development, and only few attempts have been made to include them in LCIA. Methods The approaches are described and evaluated against a set of assessment criteria comprising compatibility with the methodological requirements of LCIA, environmental relevance, reproducibility, data demand, data availability, quantification of uncertainty, transparency and spatial differentiation. Results and Discussion The results of the evaluation of the two impact approaches (i.e. PNEC and PAF) show both pros and cons for each of them. The assessment factor-based PNEC approaches have a low data demand and use only the lowest data (e.g. lowest NOEC value). Because it is developed in tiered risk assessment, and hence makes use of conservative assessment factors, it is not optimal, in its present form, to use in the comparative framework of LCIA, where best estimates are sought. The PAF approaches have a higher data demand but use all data and can be based on effect data (PNEC is no-effect-based), thus making these approaches non-conservative and more suitable for LCIA. However, indiscriminate use of ecotoxicity data tends to make the PAF-approaches no more environmentally relevant than the assessment factor-based PNEC approaches. The PAF approaches, however, can at least in theory be linked to damage modelling. All the approaches for damage modelling which are included here have a high environmental relevance but very low data availability, apart from the 'media recovery-approach', which depends directly on the fate model. They are all at a very early stage of development. Conclusion Recommendations and Outlook. An analysis of the different PAF approaches shows that the crucial point is according to which principles and based on which data the hazardous concentration to 50% of the included species (i.e. HC50) is estimated. The ability to calculate many characterisation factors for ecotoxicity is important for this impact category to be included in LCIA in a proper way. However, the access to effect data for the relevant chemicals is typically limited. So, besides the coupling to damage modelling, the main challenge within the further development and improvement of ecotoxicity effect indicators is to find an optimal method to estimate HC50 based on little data.     

Innervation of pulmonary neuroendocrine cells and neuroepithelial bodies in developing rabbit lung.

We investigated the development of innervation of the pulmonary neuroendocrine cell (PNEC) system composed of single cells and organoid cell clusters, neuroepithelial bodies (NEB) in rabbit fetal and neonatal lungs. To visualize the nerve fibers and their contacts with PNECs/NEBs, we used confocal microscopy and multilabel immunohistochemistry (IHC) with pan-neural marker, synaptic vesicle protein 2 (SV2), and serotonin (5-HT) as markers for PNECs/NEBs, and smooth muscle actin or cytokeratin to identify airway landmarks. The numbers and distribution of PNEC/NEB at different stages of lung development (E16, 18, 21, 26, and P2) and the density of innervation were quantified. First PNECs immunoreactive for 5-HT were identified in primitive airway epithelium at E18 as single cells or as small cell clusters with or without early nerve contacts. At E21 a significant increase in the number of PNECs with formation of early innervated NEB corpuscules was observed. The overall numbers of PNECs/NEBs and the density of mucosal, submucosal, and intercorpuscular innervation increased with progressing gestation and peaked postnatally (P2). At term, the majority of NEBs and single PNECs within airway mucosa possessed neural contacts. Such an extensive and complex innervation of the PNEC system indicates a multifunctional role in developing lung and during neonatal adaptation.     

Ontogeny of pulmonary neuroendocrine cells which express the alpha-subunit of guanine nucleotide-binding protein Go

 In order to ascertain that alpha-subunit of guanine nucleotide-binding protein Go (Goα)-positive cells in the lung epithelia are pulmonary neuroendocrine cells (PNECs), we carried out an immunohistochemical study in young adult and fetal lungs of rodents and in cultured fetal lung explants. Serial sections showed that Goα-positive cells were immunostained for calcitonin gene-related peptide and serotonin in young adult mouse, rat, and hamster lungs and that these cells are, therefore, PNECs. In the fetal lungs of hamster and mouse, Goα-positive PNECs appeared in the epithelium of the lobar bronchus by gestational day 13 in hamster and by day 15.5 in mouse, and they increased with a proximal-to-distal wave during the late fetal period. Explants of immature lung from the fetal hamster on gestational day 11 were cultured. After 2 days of culture, Goα-positive PNEC clusters appeared in the main and lobar bronchi and many PNEC clusters were seen after 4 days of culture. To determine the functional significance of Go in the development of the fetal lung, pertussis toxin, a Go inhibitor, was added to the medium, and changes in branching morphogenesis and PNEC development were studied. Although branching morphogenesis was not disturbed by pertussis toxin, the toxin treatment induced large PNEC clusters in the cultured lung explant. In summary, we showed that Goα is a neuroendocrine marker for PNECs and that Goα-positive cells appear along with development of PNECs in fetal hamster lung in vivo and in vitro. The functional significance of Go in the development of fetal lung is obscure, but signals mediated through this GTP-binding protein could be related to some functions of PNECs. Accepted:13 January 1999     

Assessing the Need for Groundwater Quality Guidelines for Pesticides Using the Species Sensitivity Distribution Approach

The water quality needs of groundwater ecosystems are rarely considered. It is currently assumed that water quality guidelines for surface waters will also protect groundwater ecosystems and their fauna, but this assumption has not been tested. The aim of this study is to determine whether water quality guidelines specifically for groundwater ecosystems are needed and to provide a preliminary risk assessment for groundwater ecosystems in Australia. In the absence of sufficient toxicity data for true groundwater fauna, 48–96 h LC50 data for groundwater-dwelling invertebrate orders (e.g., Crustacea, Rotifera) are used as a surrogate and were compared, using Species Sensitivity Distribution (SSD) curves, to a full suite of surface taxa (including fish, insects, and algae). SSD curves were derived for a range of pesticides previously detected in Australian groundwaters and were fitted using the Burr Type III distribution. Significant differences in the sensitivities of surface and groundwater taxa to Atrazine and Chlorpyrifos were detected, indicating surface water quality guidelines are not always suitable to protect or best manage groundwater ecosystems. Water quality guideline values derived from the SSDs highlighted a significant threat of contamination to groundwater ecosystems from agricultural chemicals. Clearly water quality guidelines specifically for groundwater ecosystems are needed.     

Effect of bisphenol A toxicity on growth performance,biochemical variables,and oxidative stress biomarkers of Nile tilapia,Oreochromis niloticus (L.)

Bisphenol A (BPA) is one of the industrial chemical compound which is used in the production of polycarbonate plastics and epoxy resins. BPA is used throughout the world and it could enter the aquatic ecosystems causing serious problems. To evaluate the potential effects of BPA toxicity on Nile tilapia, Oreochromis niloticus (L.) performance, its lethal concentration (LC₅₀) was determined and it was 13.13 µg/L. After that, fish (33.9 ± 0.55 g/fish) were exposed to 0.0, 1.64, or 3.28 µg/L of BPA for 6 weeks after which growth performance, biochemical variables, and oxidative defense system were assessed. The results showed that fish growth and feed intake were significantly reduced as BPA levels increased with no significant difference in fish survival. Total protein, albumin, globulin, and acetylcholine esterase decreased significantly; meanwhile, aspartate transferase, alanine transferase, alkaline phosphatase, uric acid, and creatinine increased significantly with exposure to BPA in a dose dependent manner. Furthermore, malondialdehyde value and the activities of superoxide dismutase and catalase increased significantly; while glutathione peroxidase and glutathione S‐transferase decreased significantly as BPA levels increased. In conclusion, BPA exposure in aquatic environment deteriorated fish performance and health causing liver and kidney dysfunction. Thus, fish exerted oxidative defense enzymes as a protection tool against BPA toxicity.     

Review: ecotoxicity of organic and organo-metallic antifouling co-biocides and implications for environmental hazard and risk assessments in aquatic ecosystems

Hazard assessments of Irgarol 1051, diuron, 2-(thiocyanomethylthio)benzothiazole (TCMTB), dichloro-octylisothiazolin (DCOIT), chlorothalonil, dichlofluanid, thiram, zinc pyrithione, copper pyrithione, triphenylborane pyridine (TPBP), capsaicin, nonivamide, tralopyril and medetomidine were performed to establish robust environmental quality standards (EQS), based on predicted no effect concentrations (PNECs). Microalgae, zooplankton, fish and amphibians were the most sensitive ecological groups to all the antifoulants evaluated, especially in the early life stages. No differences were identified between freshwater and seawater species. The use of toxicity tests with non-standard species is encouraged because they increase the datasets, allowing EQS to be derived from probabilistic-based PNECs whilst reducing uncertainties. The global ban of tributyltin (TBT) has been heralded as a major environmental success; however, substitute antifoulants may also pose risks to aquatic ecosystems. Environmental risk assessments (ERAs) have driven decision-makings for regulating antifouling products, but in many countries there is still a lack of regulation of antifouling biocides which should be addressed.     

The process of thermodialysis in bioremediation of waters polluted by endocrine disruptors

Endocrine disruptors are chemicals able to induce adverse effects into wildlife and humans owing to their ability of interfering with the endocrine system. Bisphenol A (BPA) has been chosen as model of endocrine disruptors. To reduce the BPA pollution in waters we proposed the employment of the process of thermodialysis. Two different catalytic membranes have been prepared by covalently immobilizing laccase (from Trametes versicolor) by means of a diazotation process or tyrosinase (from mushroom) by condensation. The support was a nylon membrane. The bioremediation power of both catalytic membranes has been analysed under isothermal and non-isothermal conditions.The advantages in using non-isothermal bioreactors were discussed in terms of reduction of the bioremediation times.     

Neuronal developmental marker FORSE-1 identifies a putative progenitor of the pulmonary neuroendocrine cell lineage during lung development.

The FORSE-1 (forebrain-surface-embryonic) monoclonal antibody (MAb) recognizes a carbohydrate cell surface epitope related to the Lewis-X (LeX) and stage-specific embryonic antigens (SSEAs). In the developing CNS, the FORSE-1 epitope is believed to serve as a marker of progenitor cells. We studied the expression of the FORSE-1 epitope in pulmonary neuroendocrine cells (PNECs) and related neuroepithelial bodies (NEBs), cell types implicated in paracrine regulation of lung development. We used dual immunolabeling to identify PNECs/NEBs in tissue sections from developing rabbit fetal lungs and corresponding primary lung cell cultures. During the early stage (E16), the FORSE-1 MAb labeled primitive airway epithelium, whereas serotonin (5HT) immunoreactivity, a marker of PNEC/NEB differentiation, was negative. After E18, FORSE-1 labeling became restricted to PNECs and NEBs, identified by co-expression with 5HT, then decreased coincident with an increase in 5HT. Expression of the FORSE-1 epitope correlated inversely with 5HT expression in PNEC/NEB cells. FORSE-1 immunoreactivity correlated with cell proliferation assessed by BrdU labeling. Downregulation of the FORSE-1 epitope correlated with maturation of PNECs/NEBs. The presence of few FORSE-1/5HT-positive cells in postnatal lung suggests retention of progenitors. The FORSE-1 epitope was associated with a high molecular weight (286 kD) glycoprotein that decreased with increasing gestational age, as demonstrated by immunoblotting. Overall expression of SSEA-1, -3, and -4 antigens was similar to FORSE-1/5HT, although the former was preferentially localized to neurite-like processes. Because the role of the FORSE-1 epitope in the CNS probably involves cell adhesion and differentiation, we propose a similar function in developing lung. The demonstration of LeX/SSEA antigen expression in the PNEC/NEB cell lineage underscores the importance of these cells in developing lung. Furthermore, the FORSE-1 antigen may identify committed progenitors of the PNEC/NEB cell system.     

A Weight of Evidence Analysis of the Chronic Ecotoxicity of Nonylphenol Ethoxylates,Nonylphenol Ether Carboxylates,and Nonylphenol

Nonylphenol ethoxylates (NPE) are widely used surfactant compounds with many domestic and industrial applications. Due to the nature of their use in down-the-drain applications, spent NPE are discharged to septic systems or to wastewater treatment plants. Biodegradation of parent material during treatment is often incomplete, leading to release of NPE and their degradation intermediates into the environment. Considerable aquatic toxicity research has occurred on NPE and particularly on nonylphenol (NP). Available data were subjected to a quality review and all studies of acceptable quality were used in a weight of evidence hazard assessment. Data for NP were further analyzed using a Species Sensitivities Distribution (SSD) approach. About 90 chronic values are available (ChVs, geometric mean of the no-observed effect concentration and lowest-observed effect concentration for each endpoint reported), which may be reduced to average ChVs for each tested species. Higher mole NPE (NPE ≥ 9) had ChVs ranging from 900 to 14,100 μg/L, ChVs for the low mole nonylphenol ether carboxylate (NPEC1) ranged from 3200 to 12,000 μg/L, ChVs for lower mole NPE (NPE1,2) ranged from 11 to 500 μg/L, and ChVs for NP ranged from 5 to 3500 μg/L. Using the SSD analysis for NP with higher quality study results, the 10th percentile chronic effect value is 5.7 μg/L, which supports the draft USEPA criteria on NP of 5.9 μg/L.     

Decontamination Activity of Ryegrass Exudates Towards Bisphenol A in the Absence and Presence of Dissolved Natural Organic Matter

Bisphenol A (BPA) is an endocrine disruptor compound widespread in terrestrial and aquatic systems of urbanized and industrialized regions. This study evaluated the capacity of ryegrass (Lolium perenne) aqueous exudates to degrade BPA at a concentration of 10 mg L^?1 both in the absence and in the presence of an organic fraction often coexisting with plant exudates, i.e., natural organic matter (NOM), tested at a concentration of 20 mg L^?1. In exudates alone, BPA degradation ceased after one day from the product addition when residual BPA resulted 65% of the initial BPA, whereas in exudates with the addition of NOM the degradation process continued for 4 days when residual BPA resulted 49%. Measurements of peroxidase and laccase activities in exudates suggested a significant involvement of these enzymes in BPA degradation. This finding was further confirmed by the almost complete absence of BPA degradation in aqueous exudates strongly acidified. In some BPA-contaminated exudates, chromatographic analysis revealed the presence of a newly formed compound identified as a BPA oxidation product by Fourier transform - ion cyclotron resonance mass spectrometry analysis. In conclusion, ryegrass exudates possess a relevant decontamination capacity towards BPA which persists and appears to be enhanced by the addition of NOM.     

Aquatic plant bioassays used in the assessment of water quality in German rivers

A novel aquatic bioassay with Lemna minor (duckweed), a representative of higher plants, was applied to pore waters (interstitial waters) from river sediments. The results have been used for the ecotoxicological assessment of sediments in several German rivers. The aim of the present study is to demonstrate the usefulness of a macrophyte bioassay, as a supplement to the standardised algae bioassays, with regard to the ecotoxicological assessment of aquatic systems. Results relating to the development of a sediment contact test (using the whole sediment) with Lemna minor are also presented.     

Bisphenol A exposure modifies methylation of imprinted genes in mouse oocytes via the estrogen receptor signaling pathway

Bisphenol A (BPA), a synthetic additive used to harden polycarbonate plastics and epoxy resin, is ubiquitous in our everyday environment. Many studies have indicated detrimental effects of BPA on the mammalian reproductive abilities. This study is aimed to test the potential effects of BPA on methylation of imprinted genes during oocyte growth and meiotic maturation in CD-1 mice. Our results demonstrated that BPA exposure resulted in hypomethylation of imprinted gene Igf2r and Peg3 during oocyte growth, and enhanced estrogen receptor (ER) expression at the levels of mRNA and protein. The relationship between ER expression and imprinted gene hypomethylation was substantiated using an ER inhibitor, ICI182780. In addition, BPA promoted the primordial to primary follicle transition, thereby speeding up the depletion of the primordial follicle pool, and suppressed the meiotic maturation of oocytes because of abnormal spindle assembling in meiosis I. In conclusion, neonatal exposure to BPA inhibits methylation of imprinted genes during oogenesis via the ER signaling pathway in CD-1 mice.     

Biodegradation of bisphenol A and its halogenated analogues by <Emphasis Type="Italic">Cunninghamella elegans</Emphasis> ATCC36112

Bisphenol A and its halogenated analogues are commonly used industrial chemicals with strong toxicological effects over many organisms. In this study, metabolic fate of bisphenol A and its halogenated analogues were evaluated with Cunninghamella elegans ATCC36112. Bisphenol A and related analogues were rapidly transformed into several metabolites by C. elegans within 2–4 days. Detailed analysis of metabolites reveals that both phase I and II metabolism occurred in C. elegans. Cytochrome P450-dependent hydroxylation was observed in BPA. However, major reaction with bisphenol A and analogues with 1-2 halogen atoms were the formation of glucose-conjugate, not being inhibited by cytochrome P450 inhibitor. Overall metabolic rates decreased with increasing number of substitution at 2- and 6-position of BPA structures, which may be consequences of limited bioavailability or steric hindrance to conjugate-forming reaction. Information from the current study will provide detailed insights over the fungal metabolism of BPA and analogues.     

High Intake of Dietary Sugar Enhances Bisphenol A (BPA) Disruption and Reveals Ribosome-Mediated Pathways of Toxicity

Bisphenol A (BPA) is an organic compound to which human populations are ubiquitously exposed. Epidemiological data suggest BPA exposure might be associated with higher rates of diabetes and reproductive anomalies. Health concerns also include transgenerational consequences, but these mechanisms are crudely defined. Similarly, little is known about synergistic interactions between BPA and other substances. Here we show that acute and chronic exposure to BPA causes genome-wide modulation of several functionally coherent genetic pathways in the fruit fly Drosophila melanogaster. In particular, BPA exposure causes massive downregulation of testis-specific genes and upregulation of ribosome-associated genes widely expressed across tissues. In addition, it causes the modulation of transposable elements that are specific to the ribosomal DNA loci, suggesting that nucleolar stress might contribute to BPA toxicity. The upregulation of ribosome-associated genes and the impairment of testis-specific gene expression are significantly enhanced upon BPA exposure with a high-sugar diet. Our results suggest that BPA and dietary sugar might functionally interact, with consequences to regulatory programs in both reproductive and somatic tissues.     

Predictive Value of Species Sensitivity Distributions for Effects of Herbicides in Freshwater Ecosystems

In this article we present a review of the laboratory and field toxicity of herbicides to aquatic ecosystems. Single-species acute toxicity data and (micro)mesocosm data were collated for nine herbicides. These data were used to investigate the importance of test species selection in constructing species sensitivity distributions (SSDs), and in estimating hazardous concentrations (i.e., HC5) protective for freshwater aquatic ecosystems. A lognormal model was fitted to toxicity data (acute EC50s and chronic NOECs) and the resulting distribution used to estimate lower (95% confidence), median (50% confidence), and upper (5% confidence), HC5 values. The taxonomic composition of the species assemblage used to construct the SSD does have a significant influence on the assessment of hazard and only sensitive primary producers should be included for the risk assessment of herbicides. No systematic difference in sensitivity between standard and non-standard test species was observed. Hazardous concentrations estimated using laboratory-derived acute and chronic toxicity data for sensitive freshwater primary producers were compared to the response of herbicide-stressed freshwater ecosystems using a similar exposure regime. The lower limit of the acute HC5 and the median value of the chronic HC5 were protective of adverse effects in aquatic micro/mesocosms even under a long-term exposure regime. The median HC5 estimate based on acute data was protective of adverse ecological effects in freshwater ecosystems when a pulsed or short-term exposure regime was used in the microcosm and mesocosm experiments. There was also concordance between the predictions from the effect model PERPEST and the concentrations at which clear effects started to emerge in laboratory and field studies. However, compared to the SSD concept, the PERPEST model is able to provide more information on ecological risks when a common toxicological mode of action is evaluated as it considers both recovery and indirect effects.     

基于氧化应激与细胞凋亡探究双酚A慢性暴露致小鼠肾毒性作用机制

双酚A (bisphenol A, BPA)被广泛应用于生产环氧树脂和聚碳酸酯塑料等制品,在强酸、强碱或高温条件下,BPA被释放出来,然后渗入环境中。在大多数生物液体中都检测到了不同浓度的BPA,BPA的存在已被证明与许多慢性疾病密切相关,包括慢性肾病(chronic kidney disease,CKD)。然而,关于BPA的有害作用及其对CKD的不良影响知之甚少。为了探讨BPA对动物肾毒性的作用机制,本研究通过向饮水中加入0.01、0.1和1 mg/L的BPA,暴露于雌性小鼠4周后,交配和怀孕的雌性小鼠持续接触BPA,直到断奶;F1代3周龄雄性仔鼠继续口服相同剂量的BPA,持续10周。结果表明,0.1mg/L和1mg/LBPA处理组小鼠的肾脏损伤严重,血清中肾脏功能指标尿素氮(urea nitrogen,UN)、肌酐(creatinine,CR)和尿酸(uric acid,UA)的含量均发生显著升高(P<0.05);肾脏组织形态结构被损害;肾脏抗氧化相关基因在mRNA和蛋白水平上的表达显著降低(P<0.05),包括谷胱甘肽硫转移酶(glutathione-S-transf...