Lucy E. J. Lee

A European perspective on alternatives to animal testing for environmental hazard identification and risk assessment

Tests with vertebrates are an integral part of environmental hazard identification and risk assessment of chemicals, plant protection products, pharmaceuticals, biocides, feed additives and effluents. These tests raise ethical and economic concerns and are considered as inappropriate for assessing all of the substances and effluents that require regulatory testing. Hence, there is a strong demand for replacement, reduction and refinement strategies and methods. However, until now alternative approaches have only rarely been used in regulatory settings. This review provides an overview on current regulations of chemicals and the requirements for animal tests in environmental hazard and risk assessment. It aims to highlight the potential areas for alternative approaches in environmental hazard identification and risk assessment. Perspectives and limitations of alternative approaches to animal tests using vertebrates in environmental toxicology, i.e. mainly fish and amphibians, are discussed. Free access to existing (proprietary) animal test data, availability of validated alternative methods and a practical implementation of conceptual approaches such as the Adverse Outcome Pathways and Integrated Testing Strategies were identified as major requirements towards the successful development and implementation of alternative approaches. Although this article focusses on European regulations, its considerations and conclusions are of global relevance.

The Use of Fish‐Derived Cell Lines for Investigation of Environmental Contaminants

This unit describes protocols for growing salmonid cell lines and using them in in vitro toxicology studies. Cell viability of cultures is assessed with three indicator dyes: alamar blue for metabolic activity, CFDA‐AM for membrane integrity, and neutral red for lysosomal activity. These protocols are essential tools for investigating environmental toxicity at the cellular level.

Developing a list of reference chemicals for testing alternatives to whole fish toxicity tests

This paper details the derivation of a list of 60 reference chemicals for the development of alternatives to animal testing in ecotoxicology with a particular focus on fish. The chemicals were selected as a prerequisite to gather mechanistic information on the performance of alternative testing systems, namely vertebrate cell lines and fish embryos, in comparison to the fish acute lethality test. To avoid the need for additional experiments with fish, the U.S. EPA fathead minnow database was consulted as reference for whole organism responses. This database was compared to the Halle Registry of Cytotoxicity and a collation of data by the German EPA (UBA) on acute toxicity data derived from zebrafish embryos. Chemicals that were present in the fathead minnow database and in at least one of the other two databases were subject to selection. Criteria included the coverage of a wide range of toxicity and physico-chemical parameters as well as the determination of outliers of the in vivo/in vitro correlations. While the reference list of chemicals now guides our research for improving cell line and fish embryo assays to make them widely applicable, the list could be of benefit to search for alternatives in ecotoxicology in general. One example would be the use of this list to validate structure-activity prediction models, which in turn would benefit from a continuous extension of this list with regard to physico-chemical and toxicological data.

Establishment of long term cultures of neural stem cells from adult sea bass, Dicentrarchus labrax.

Long term cell cultures could be obtained from brains of adult sea bass (Dicentrarchus labrax) up to 5 days post mortem. On three different occasions, sea bass brain tissues were dissected, dispersed and cultured in Leibovitzs L-15 media supplemented with 10% fetal bovine serum. The resulting cellular preparations could be passaged within 2 or 3 weeks of growth. The neural cells derived from the first trial (SBB-W1) have now been passaged over 24 times within two years. These cells have been cryopreserved and thawed successfully. SBB-W1 cells are slow growing with doubling times requiring at least 7 days at 22 degrees C. These long term cell cultures could be grown in suspension as neurospheres that were immunopositive for nestin, a marker for neural stem cells, or grown as adherent monolayers displaying both glial and neural morphologies. Immunostaining with anti-glial fibrillary acidic protein (a glial marker) and anti-neurofilament (a neuronal marker), yielded positive staining in most cells, suggesting their possible identity as neural stem cells. Furthermore, Sox 2, a marker for neural stem cells, could be detected from these cell extracts as well as proliferating cell nuclear antigen, a marker for proliferating cells. SBB-W1 could be transfected using pEGFP-N1 indicating their viability and suitability as convenient models for neurophysiological or neurotoxicological studies.

Long-term storage and impedance-based water toxicity testing capabilities of fluidic biochips seeded with RTgill-W1 cells

Rainbow trout gill epithelial cells (RTgill-W1) are used in a cell-based biosensor that can respond within one hour to toxic chemicals that have the potential to contaminate drinking water supplies. RTgill-W1 cells seeded on enclosed fluidic biochips and monitored using electric cell-substrate impedance sensing (ECIS) technology responded to 18 out of the 18 toxic chemicals tested within one hour of exposure. Nine of these chemical responses were within established concentration ranges specified by the U.S. Army for comparison of toxicity sensors for field application. The RTgill-W1 cells remain viable on the biochips at ambient carbon dioxide levels at 6°C for 78weeks without media changes. RTgill-W1 biochips stored in this manner were challenged with 9.4μM sodium pentachlorophenate (PCP), a benchmark toxicant, and impedance responses were significant (p<0.001) for all storage times tested. This poikilothermic cell line has toxicant sensitivity comparable to a mammalian cell line (bovine lung microvessel endothelial cells (BLMVECs)) that was tested on fluidic biochips with the same chemicals. In order to remain viable, the BLMVEC biochips required media replenishments 3 times per week while being maintained at 37°C. The ability of RTgill-W1 biochips to maintain monolayer integrity without media replenishments for 78weeks, combined with their chemical sensitivity and rapid response time, make them excellent candidates for use in low cost, maintenance-free field-portable biosensors.

The Use of Fish-Derived Cell Lines for Investigation of Environmental Contaminants: An Update Following OECD's Fish Toxicity Testing Framework No. 171

Protocols for evaluating chemical toxicity at the cellular level using fish cell lines are described in this unit. Routine methodologies for growing salmonid cell lines, and using them in aquatic toxicology studies that support the mandate of the Organization for Economic Co‐operation and Development (OECD) to reduce the use of whole animals in toxicity testing, are presented. Rapid, simple, cost‐effective tests evaluating viability of cells with three indicator dyes per sample provides a broad overview of the sensitivity of cells to chemical contaminants. This fluorometric assay involves: (1) alamar blue for metabolic activity, (2) CFDA‐AM for membrane integrity, and (3) neutral red for lysosomal function. These protocols are conveniently performed in semi‐unison within the same multiwell plates and read at three different wavelengths. Detailed step‐by‐step descriptions of the assays, parameters to consider, troubleshooting, and guidelines for data interpretation are provided as essential tools for investigating environmental aquatic contaminants at the cellular level. Curr. Protoc. Toxicol. 56:1.5.1‐1.5.20.

Initiation of a Zebrafish Blastula Cell Line on Rainbow Trout Stromal Cells and Subsequent Development Under Feeder-Free Conditions into a Cell Line, ZEB2J

A continuous cell line, ZEB2, was developed from zebrafish blastula-stage embryos expressing enhanced green fluorescent protein (GFP). Originally the rainbow trout spleen cell line, RTS34st, was used as feeders to initiate and maintain the cells through several passages. ZEB2 was then grown for 2 years without feeders in L-15 with 15% fetal bovine serum (FBS) for 120 population doublings. This new cell line, ZEB2J, was heteroploid, had detectable telomerase activity, and was adherent. After growing into monolayers, some cells continued to grow into mounds. Cultures expressed Pou-2 mRNA and contained many alkaline phosphatase and a few stage-specific embryonic antigen-1-positive cells. In dishes coated with a phospholipid polymer (2-methacryloxyloxyethyl phosphorylcholine, MPC), ZEB2J formed spherical aggregates. Aggregates attached to conventional culture plastic, and most cells that emerged from aggregates had typical epithelial-like shapes of ZEB2J, which suggests that ZEB2J had limited differentiation potential, despite expressing some stem cell properties. The fluorescence of ZEB2J allowed relationships with feeder cells to be studied. In MPC dishes, ZEB2J formed mixed spheroids with RTS34st. In adherent cocultures, RTS34st and other fish cell lines strongly stimulated the ZEB2J growth, which could be quantified specifically because ZEB2J expressed GFP. ZEB2J should be useful for optimizing culture conditions for zebrafish embryonic stem cells.

Use of Tetrahymena thermophila to study the role of protozoa in inactivation of viruses in water.

ABSTRACT The ability of a ciliate to inactivate bacteriophage was studied because these viruses are known to influence the size and diversity of bacterial populations, which affect nutrient cycling in natural waters and effluent quality in sewage treatment, and because ciliates are ubiquitous in aquatic environments, including sewage treatment plants. Tetrahymena thermophila was used as a representative ciliate; T4 was used as a model bacteriophage. The T4 titer was monitored on Escherichia coli B in a double-agar overlay assay. T4 and the ciliate were incubated together under different conditions and for various times, after which the mixture was centrifuged through a step gradient, producing a top layer free of ciliates. The T4 titer in this layer decreased as coincubation time increased, but no decrease was seen if phage were incubated with formalin-fixed Tetrahymena. The T4 titer associated with the pellet of living ciliates was very low, suggesting that removal of the phage by Tetrahymena inactivated T4. When Tetrahymena cells were incubated with SYBR gold-labeled phage, fluorescence was localized in structures that had the shape and position of food vacuoles. Incubation of the phage and ciliate with cytochalasin B or at 4°C impaired T4 inactivation. These results suggest the active removal of T4 bacteriophage from fluid by macropinocytosis, followed by digestion in food vacuoles. Such ciliate virophagy may be a mechanism occurring in natural waters and sewage treatment, and the methods described here could be used to study the factors influencing inactivation and possibly water quality.

A teleost in vitro reporter gene assay to screen for agonists of the peroxisome proliferator-activated receptors.

Several contaminants detected in aquatic ecosystems are agonists of peroxisome proliferator-activated receptors (PPARs). Peroxisome proliferator-activated receptors interact with the retinoid X receptor (RXR) to activate the transcription of genes that control a variety of physiological functions. We cloned and sequenced partial cDNA fragments of rainbow trout (Oncorhynchus mykiss) PPARalpha and PPARbeta from rainbow trout (rt) gill-W1 cells, a cell line derived from rainbow trout gills; predicted amino acid identities are 77% and 82% compared with their respective human homologs and 83 to 88% and 91 to 98% identical to fish homologs. A reporter gene assay was developed by transfecting rt-gill-W1 cells with a reporter gene construct containing the peroxisome proliferator response element (PPRE) of the rat liver 3-ketoacyl-CoA thiolase B (TB) gene, which drives luciferase expression. Agonists of both PPARalpha (WY14,643 and gemfibrozil) and PPARbeta (bezafibrate) induced luciferase activity, while rosiglitazone, a PPARgamma agonist, was not effective. The fibrate drug, bezafibrate increased luciferase activity in a dose-dependent manner, but addition of 50 nM 9-cis-retinoic acid to the transfected rt-gill-W1 cell culture maximized the sensitivity of the assay so that bezafibrate could be detected at concentrations as low as 6 nM. Extracts from treated domestic wastewater containing fibrate drugs induced luciferase activity in the transfected gill cells. This in vitro reporter gene assay shows promise as a rapid and sensitive technique for screening environmental samples for PPAR-active substances.

Animal cell cultures in microsporidial research: their general roles and their specific use for fish microsporidia

The use of animal cell cultures as tools for studying the microsporidia of insects and mammals is briefly reviewed, along with an in depth review of the literature on using fish cell cultures to study the microsporidia of fish. Fish cell cultures have been used less often but have had some success. Very short-term primary cultures have been used to show how microsporidia spores can modulate the activities of phagocytes. The most successful microsporidia/fish cell culture system has been relatively long-term primary cultures of salmonid leukocytes for culturing Nucleospora salmonis. Surprisingly, this system can also support the development of Enterocytozoon bienusi, which is of mammalian origin. Some modest success has been achieved in growing Pseudoloma neurophilia on several different fish cell lines. The eel cell line, EP-1, appears to be the only published example of any fish cell line being permanently infected with microsporidia, in this case Heterosporis anguillarum. These cell culture approaches promise to be valuable in understanding and treating microsporidia infections in fish, which are increasingly of economic importance.