Macondo crude oil from the Deepwater Horizon oil spill disrupts specific developmental processes during zebrafish embryogenesis

T Yvanka de Soysa; Allison Ulrich; Timo Friedrich; Danielle Pite; Shannon L Compton; Deborah Ok; Rebecca L Bernardos; Gerald B Downes; Shizuka Hsieh; Rachael Stein; M Caterina Lagdameo; Katherine Halvorsen; Lydia-Rose Kesich; Michael JF Barresi

doi:10.1186/1741-7007-10-40

Research article
Open Access
Published: 04 May 2012

Macondo crude oil from the Deepwater Horizon oil spill disrupts specific developmental processes during zebrafish embryogenesis

BMC Biology volume 10, Article number: 40 (2012) Cite this article

16k Accesses
57 Citations
23 Altmetric
Metrics details

Abstract

Background

The Deepwater Horizon disaster was the largest marine oil spill in history, and total vertical exposure of oil to the water column suggests it could impact an enormous diversity of ecosystems. The most vulnerable organisms are those encountering these pollutants during their early life stages. Water-soluble components of crude oil and specific polycyclic aromatic hydrocarbons have been shown to cause defects in cardiovascular and craniofacial development in a variety of teleost species, but the developmental origins of these defects have yet to be determined. We have adopted zebrafish, Danio rerio, as a model to test whether water accumulated fractions (WAF) of the Deepwater Horizon oil could impact specific embryonic developmental processes. While not a native species to the Gulf waters, the developmental biology of zebrafish has been well characterized and makes it a powerful model system to reveal the cellular and molecular mechanisms behind Macondo crude toxicity.

Results

WAF of Macondo crude oil sampled during the oil spill was used to treat zebrafish throughout embryonic and larval development. Our results indicate that the Macondo crude oil causes a variety of significant defects in zebrafish embryogenesis, but these defects have specific developmental origins. WAF treatments caused defects in craniofacial development and circulatory function similar to previous reports, but we extend these results to show they are likely derived from an earlier defect in neural crest cell development. Moreover, we demonstrate that exposure to WAFs causes a variety of novel deformations in specific developmental processes, including programmed cell death, locomotor behavior, sensory and motor axon pathfinding, somitogenesis and muscle patterning. Interestingly, the severity of cell death and muscle phenotypes decreased over several months of repeated analysis, which was correlated with a rapid drop-off in the aromatic and alkane hydrocarbon components of the oil.

Conclusions

Whether these teratogenic effects are unique to the oil from the Deepwater Horizon oil spill or generalizable for most crude oil types remains to be determined. This work establishes a model for further investigation into the molecular mechanisms behind crude oil mediated deformations. In addition, due to the high conservation of genetic and cellular processes between zebrafish and other vertebrates, our work also provides a platform for more focused assessment of the impact that the Deepwater Horizon oil spill has had on the early life stages of native fish species in the Gulf of Mexico and the Atlantic Ocean.

Introduction

More than 200 million gallons of crude oil were released from the Macondo Well in the Gulf of Mexico during the 2010 Deepwater Horizon oil spill [1, 2]. The oil gushed from approximately 5,000 feet below the surface creating underwater plumes of oil and slicks on both the ocean floor and surface. The oil's total vertical exposure to the water column suggested it had the potential to impact a diversity of ecosystems in the Gulf of Mexico and Atlantic Ocean from coastal wetlands to coral reefs to deep-water benthic communities [3, 4]. In fact, many thousands of invertebrate and vertebrate carcasses have been discovered and attributed to the Macondo oil, and due to the wide-spread and hidden nature of this disaster, species mortality rates are hypothesized to be at least 50 times underrepresented [4, 5].

Of particular concern is how embryos and larvae will be affected by this oil spill, as organisms in these early life stages are typically unable to flee a contaminated area and lack the tissue mass and mature detoxification systems necessary to withstand toxic insults. Furthermore, loss of whole clutches of embryos and larvae can have catastrophic consequences for population dynamics over long time periods [6]. The National Oceanic and Atmospheric Administration (NOAA) reported an unusually high number of stillborn and newborn dolphins that began washing up on the Gulf shores starting in January 2011 [7]. While only a small number of these dead dolphins had obvious signs of oil exposure, the timing suggests an association between the gestational period of dolphin embryonic and fetal development with the Deepwater Horizon blowout and oil spill [4]. There are 52 taxa of native fish species also known to spawn in the Gulf of Mexico such as tuna, red snapper and yellowfin groupers [8], and unfortunately little is known about how the Macondo crude oil might directly impact early development of dolphins or these fish species. It will be critically important to identify the molecular targets of crude oil toxicants that effect embryonic development to provide greater predictive power in the risk assessment of this and future spills.

Exposure to crude oil and/or the water-soluble, polycyclic aromatic hydrocarbons (PAH) that make up much of the oil have been shown to cause cardiovascular abnormalities and pericardial edema in topsmelt and Pacific herring embryos, as well as additional defects in jaw and spinal cord development in the crimson-spotted rainbow fish [9–11]. Whether oil from the Macondo well can cause similar defects in embryonic development needs to be determined. The majority of research using native Gulf fish species to determine the effects of crude oil on embryonic development has been limited to the analysis of mortality and gross morphological changes. However, the relatively recent characterization of zebrafish (Danio rerio) as a laboratory fish model system has revealed significant insights into the developmental mechanisms governing embryogenesis [12, 13]. Zebrafish provide researchers with the consistent accessibility of genetically defined lines of embryos and a battery of reliable genetic, molecular and cellular techniques for higher resolution analysis, benefits that are providing significant advantages to the use of zebrafish in toxicology. The small adult fish size, large embryo clutches, ex utero development, and transparent embryo and larval stages of zebrafish enable cost effective maintenance of many fish, reproducible sample sizes, simple application of toxin treatments, and easy evaluation of end-point toxicity [14–18]. The use of zebrafish to assay drug and pollutant toxicity has already provided insights into the developmental and molecular mechanistic roles of metals [19, 20], dioxins [21–24], pesticides [25, 26], endocrine disruptors [27, 28], alcohols [29–31], chemotherapies [32–34] and specific pharmaceutical compounds many of which were assessed via high-throughput screening [35].

Examination of the effect of crude oil and its more common PAHs on zebrafish embryos has shown developmental abnormalities that include cardiac edema, reduced jaw development, curvature of the spine, hemorrhaging, reduced larval heart rate and cardiac arrhythmia [6, 36–39]. While these varied deformations are clearly attributed to crude oil exposure, it is unknown what early embryonic processes at the cellular or molecular levels are directly affected. Further investigations utilizing zebrafish to elucidate the molecular mechanisms that interact with and mediate crude oil effects could guide future preventative measures to oil spills and their clean up procedures, as well as yield new strategies to combat the teratogenesis associated with oil spill exposure.

In the present study, we sought to determine whether water-soluble components of the crude oil from the Deepwater Horizon oil spill could disrupt normal embryonic and larval development in zebrafish. Embryos were exposed to water accumulated fractions (WAFs) made from crude oil sampled from the riser insertion tube attached to the Macondo well during the 2010 oil spill. Using an array of high resolution assays to characterize a variety of discrete developmental processes, we show that the Macondo oil does not cause general and wide-spread toxicity but rather disrupts specific developmental processes, some of which have never been reported previously for any crude oil source. We show that WAF-induced deformations in cardiovascular and craniofacial development, observed in this and likely other studies [6, 36–39], are associated with reductions in specific rostral migratory streams of cranial neural crest cells. Surprisingly, Macondo oil exposure also generated novel phenotypes in apoptosis, sensory and motor axon pathfinding, somitogenesis and muscle fiber type development, which provide causative evidence for the locomotor swimming behaviors exhibited by WAF-treated embryos. Lastly, we demonstrate that dose and timing of WAF exposure are equally important for the induction of cell death and muscle specific phenotypes. Our results suggest that crude oil components may interact with important molecular mechanisms to influence embryogenesis. The severe teratogenic effects in zebrafish associated with the Deepwater Horizon oil are cause for concern if native fish species in the Gulf of Mexico responded similarly. Finally, our findings provide a more comprehensive phenotypic map to assess pollution effects on development.

Results

Gross morphological deformations

Water accumulated fractions (WAF) of the Macondo crude oil were vortex mixed in embryo medium at a 1:10 dilution in accordance with conventional methods [40]. Analysis of different mixing procedures and serial dilution experiments were performed and are described in Additional files 1 and 2. Based on our dose response analysis we conducted all embryo treatments at the 100% concentration of the vortex-mixed, 1:10 WAF stock solution, which will from here on be referred to as WAF. Only during our analysis of locomotor behavior was 50% WAF solution used. These WAF preparations serve to model the portions of the Macondo crude oil sampled from the riser insertion tube during the Deepwater Horizon oil spill that are capable of dissolving in embryo medium. It is important to acknowledge that according to communications with BP during the period of 2 and 3 May 2010 when this sample was being collected Nalco EC9323A defoamer was being applied topside and methanol with VX9831 oxygen scavenger/catalysts solution injected subsea. While we cannot rule out the possibility that these additional agents in the vicinity of the spill site could be present in this sample, it is highly unlikely due to the method of direct sampling through the riser tube.

Embryos exposed to WAF starting at 3.5 hours post-fertilization (hpf) until a maximum of 5 days post-fertilization (dpf) caused an array of morphological phenotypes that included dorsal tail curvature, cardiac edema, cyst formation, reduced head structures and brain hemorrhages (Figure 1). More specifically, WAF-treated embryos showed moderate (Figure 1F) to severe cardiac edema (Figure 1C-E, arrows) that, in some cases, also included yolk sac edema (Figure 1C, right most arrow). In addition, a dorsal curling of the tail and caudal cyst formation were variably observed within a treated clutch of embryos but were consistently present across treatments (Figure 1E, F, double arrows; Figure 1C, D, F, arrowhead). Qualitatively, the overall size of the brain and eyes were often reduced, which was most apparent in the ventral jaw structures (Figure 1G, H, brackets). Equally obvious was the average 28% of embryos with brain hemorrhages present in the forebrain, midbrain, or hindbrain regions (Control 0.0%, n = 452; WAF, n = 441; Figure 1H-J, arrowheads). While the eyes of some WAF-treated embryos were noticeably smaller, the mean measurements of the area and perimeter of the retina and lens showed only subtle, but statistically significant, reductions in size (Figure 1K-M). These varied, but relatively specific, morphological deformations suggest that certain embryonic processes may be affected by exposure to Macondo crude oil.

Chemical analysis of water accumulated fraction

To determine what components of the crude oil were released into the WAF mixture and thus exposed to the embryos during experimental treatments, WAF samples were analyzed within one hour of being made using solid phase microextraction (SPME, 100 mm polydimethylsiloxane) and gas chromatography mass spectrometry (GCMS, Agilent 7890A GC/5975C MSD). Chemical analysis confirmed the presence of n-hexane, toluene, xylene, benzene, naphthalene and ethylbenzene that were reported by BP to be present in this source oil B. This analysis also revealed a variety of additional components, of which the most prominent were aromatics and alkanes (Figure 2A), as observed in chemical analyses of Gulf of Mexico waters after the Deepwater Horizon blowout [41–43]. Aromatic concentrations were similar over the four WAF solutions sampled (Figure 2A). We interpret the large variation in heavier alkane concentrations (Figure 2A) to the inclusion of a non-aqueous phase, into which these poorly soluble components fractionate. Such partitioning of these less-soluble components into deep-plume oil droplets [42] and into the surface slick [43] was observed in the Gulf of Mexico after the BP Oil Spill. For a full detailed report of the chemical analysis obtained see Additional file 2.

To determine how component concentrations changed with time, samples from a WAF solution were taken every five hours from petri dishes maintained under the same conditions as the treated zebrafish embryos. As demonstrated by a few selected representative components, there is a dramatic drop-off in concentrations with time (Figure 2B). For aromatics (blue), the drop-off is less extreme for the heavier napthalenes (75 to 80% drop in five hours), compared to the lighter alkylated benzenes (93 to 95% drop in five hours). The initial concentrations for the heavy alkanes (red) are beyond reported hydrocarbon solubilities, such that the WAF solution is likely to have been initially fully saturated with these poorly soluble components (as discussed further in Additional files 1 and 2). Assuming initial saturation, the drop-off for tetradecane is similar to the heavier napthalenes, at 75% within five hours. These results suggest that while embryos are initially exposed to high levels of hydrocarbon compounds, within the 5- to 10-hour window, they are experiencing hydrocarbon concentrations that approach levels observed in underwater plumes in the Gulf of Mexico [41, 42] and those along the Louisiana marshes capable of altering gene expression in adult killifish [44]. For example, within 10 hours, our concentrations of toluene, ethylbenzene and total xylenes fall below ranges observed in underwater plumes [42].

Cell proliferation and cell death

We next wanted to characterize the gross morphological phenotypes we observed at higher resolution to glean better insight into whether exposure to Macondo oil affected specific developmental processes during zebrafish embryogenesis. WAF-treated embryos exhibit subtle reductions in brain and eye size and changes to the symmetric elongation of the tail (Figure 1), all of which could indicate reductions in cell numbers. No obvious greying of tissue, indicative of cell necrosis, was ever observed in WAF treated embryos; reduction in tissue size could be attributed to either reduced cell proliferation or increased programmed cell death.

Embryos treated with WAF from 3.5 hpf to 30 hpf were immunolabeled for Phosphorylated Histone H3 (PH3) to visualize all cells undergoing mitosis [45]. Pooled averaging of three replicate WAF treatments did not show significant changes in the number of PH3-positive cells as compared to untreated controls (Figure 3A, B; control, 79.9; WAF, 76.2; t-test, P = 0.18). To control for the presence of outlying values, the lack of statistical significance was confirmed with a non-parametric test (Mann-Whitney, P = 0.0511). If mitotic rates are not altered in WAF-treated embryos, then reductions in tissue size may be due to increased apoptosis or programmed cell death.

To test whether cells were dying by apoptosis we immunolabeled embryos for Activated Caspase 3, which is a marker for cells undergoing programmed cell death [46]. Pooled averaging of four replicate experiments did show a statistically significant increase in the number of dying cells positive for Activated Caspase 3 along the trunk in WAF-treated embryos as compared to controls (Figure 3C; control, 1.94; WAF, 12.9; t-test, P = 0.0001). Apoptotic cells were present both inside and outside the spinal cord (Figure 3D-F). Interestingly, despite using the same crude oil source for each WAF preparation, the number of apoptotic cells in WAF-treated embryos decreased with each successive replicate experiment (Figure 3C). In the first treatment an average of 38.25 Activated Caspase 3-positive cells were seen in WAF-treated embryos (Control, 3.9; t-test P = 0.0001), and in the second treatment this average dropped to eight cells (Control, 2.05; t-test P = 0.0062). Furthermore, in the third and fourth replicate experiments the number of apoptotic cells in WAF-treated embryos was no longer statistically different from their respective controls (Rep3: control, 1.1; WAF, 3.05 t-test P = 0.0966; Rep4: control, 0.7; WAF, 2.15; t-test P = 0.1151). A total of 20 embryos were examined for each condition in each separate replicate experiment.

The prevalence of WAF-induced cell death during the initial experiments suggests our crude oil sample was changing and becoming less potent over time. Chemical analysis did show much of the aromatics and alkanes in the WAF drop off dramatically within five hours after exposure to the embryos (Figure 2B), thus it is possible that our crude oil source sample experienced an incremental loss of some compounds over the course of storage. To test this hypothesis directly, we treated embryos with WAF from 3.5 hpf to 18.5 hpf and then replaced this solution with a freshly mixed WAF solution and continued the experiment until 30 hpf. This WAF refreshing protocol did show a statistically significant increase in the number of Activated Caspase 3 cells (36.74 cells; n = 42) as compared to untreated (1.75 cells; n = 40) or non-refreshed WAF treated controls (11.97 cells; n = 38) (Kruskal-Wallis Test P < 0.0005) (Figure 3G-I). In fact, the number of apoptotic cells in the refreshed WAF experiment was similar to the initial WAF experiment (Rep1, 38.25 cells; P = 0.2276) (Figure 3C). This result suggests refreshing the WAF solution returned the cell death-inducing properties of the crude oil.

Circulation and vasculogenesis

We have demonstrated that embryos treated with WAF derived from the Macondo Oil exhibit cardiac edema and hemorrhaging in the brain (Figure 1). We next wanted to determine whether the Macondo Oil WAF likewise interferes with the proper development and physiology of the circulatory system that has been demonstrated previously for other crude oil types and components [9, 10, 36–39, 47, 48]. Closer examination for the presence of blood through whole-mount hemoglobin stained control and WAF-treated embryos showed a qualitative reduction in the amount of blood cells in treated embryos (Figure 4A-D). This reduction was particularly obvious in the vasculature of the pharyngeal arches (Figure 4A, B, brackets; C, arrowheads, D). Importantly, significant hemoglobin staining was still present in the common cardinal vein distal to and including the heart, but abruptly ended in the heart or bulbus artery prior to filling the aortic arches (Figure 4A-D, arrow).

The reduced blood volume specifically beyond the heart could be due to diminished hematopoiesis, improper vessel formation or altered heart function. To better discern between these possibilities, we conducted angiography with fluorescent quantum dots in 72 hpf live embryos treated with WAF starting at 3.5 hpf. This procedure was done in tg[fli:eGfp] transgenic larvae, which allowed for visualization of green endothelial cells as the red quantum dots flowed throughout the circulatory system, illuminating both the extent of circulatory function and blood vessel anatomy [49]. Imaging of the aortic arches revealed that in some cases the endothelial vasculature was present and capable of supporting circulation (Figure 4E, G, arrows and arrowheads), while in more severe cases the more posterior arch vasculature was lost and circulation was significantly reduced in the remaining vasculature (Figure 4F, H). In addition, there was often a build-up of the quantum dots in the heart atrium paired with a reduced flow of these quantum dots into the ventricle (H', dashed line). These results suggest that the endothelial vasculature and proper heart development and function are all variably compromised in WAF-treated embryos. Further supporting these results, real time imaging of blood flow through the dorsal aorta showed that individual blood cells from 60 different WAF-treated embryos (3 replicates) took, on average, 2.68 times longer to travel the distance of 7 somites (Figure 4I-K; Control, 1.44s; WAF, 3.85s; t-test, P = 0.0001).

Continued analysis of quantum dot circulation and endothelial vasculature in the trunk revealed additional phenotypes involving intersegmental blood vessel development. The most prevalent phenotype was varied frequency of reduced circulation of fluorescent quantum dots through the intersegmental blood vessels, such that vessels showed either a complete absence of flow (Figure 4L-O, arrowheads), truncated flow (Figure 4L-O, arrows), or normal circulation. Interestingly some vessels devoid of any quantum dots often showed ectopic branching and an overall improper vessel pattern (Figure 4N', O'). These phenotypes were consistent over three separate experimental replicates with at least 10 embryos imaged per replicate. As a whole, these results suggest the Macondo crude oil is capable of causing specific deformations in vasculogenesis in both the trunk and head of zebrafish that leads to reduced circulatory function.

Craniofacial development

Due to the vascular defects associated with pharyngeal arches, we next examined whether exposure to Macondo crude oil similarly causes defects in craniofacial development, a phenotype known to occur with specific PAH exposure [11, 36]. We treated embryos from 3.5 hpf to 4 dpf and then performed Alcian Blue staining to visualize cartilage [50]. Consistent with head vasculature phenotypes, WAF-treated larvae showed a range of head and jaw cartilage phenotypes (Figure 5A-F). WAF-treated embryos had a general size reduction in all cartilage elements with a significant lack of anterior extension of the most prominent jaw elements (Meckel's and ceratohyal cartilage) (Figure 5B, C, E, F). The most severely affected embryos showed dramatic reduction in all of the pharyngeal arch cartilage elements (ceratobranchial) with a complete loss of the most posterior three arches as compared to untreated control larvae (Figure 5A, B, E). In addition, we report here for the first time, in response to any crude oil treatment, a lack of anterior midline fusion of the basihyal cartilage (Figure 5E, arrowhead). Less severely affected embryos, however, did not display this basihyal phenotype (Figure 5F).

Because of the corresponding deformations in both endothelial and cartilage cell development in the head, we next hypothesized that these phenotypes may be derived from an earlier defect in the differentiation or migration of neural crest cells, which are a common progenitor cell contributing to pharyngeal arch cartilage, smooth muscle of the pharyngeal arch arteries as well as portions of the heart such as the arterial pole and endocardial cushions [51–56]. To test this we conducted whole-mount in situ hybridizations for crestin transcripts in WAF-treated and control embryos at 27 hpf. crestin is a known marker of neural crest cells during their early specification, delamination from the dorsal neural tube, and subsequent migration into the characterized pathways of the trunk and head [57]. Interestingly, embryos treated with WAF from 3.5 hpf to 27 hpf of development showed qualitative reductions in crestin-labeled cells, specifically in the anterior migratory streams known to populate the pharyngeal arches (Figure 5G-L; H, J, L, arrowheads and bracket). In contrast, the amount and position of crestin-positive cells in the trunk qualitatively appeared normal (Figure 5G, I, K, insets).

To confirm that deformations in pharyngeal arch development were associated with defects in early cranial neural crest populations, we examined the presence of rostral migratory streams of neural crest cells in tg(fli:GFP) transgenic embryos and whether they appropriately expressed the cell specification marker dlx2 [58, 59]. A total of 76% of WAF treated embryos (n = 83) showed a specific loss of one of the more posterior pharyngeal arches (Figure 5M, N, arrows) (control = 8.6%; n = 83; P < 0.0005). Importantly, despite normal dlx2 expression in the forebrain, 89.4% of WAF-treated embryos (n = 94) showed a significant reduction of dlx2 expression in all of the rostral migratory streams with a near complete absence in the presumptive posterior-most arch locations (Figure 5O, P, bracket) (control = 15.6%; n = 122; P < 0.0005). These findings suggest that Macondo crude oil is compromising the early development of cranial neural crest cell differentiation, which results in reduced posterior pharyngeal arches and the more visible defects in the heart, arch vasculature and craniofacial development.

Locomotor behavior

During our many WAF treatments it was clearly evident embryos displayed irregular swimming behaviors. The locomotor escape response to stimuli is an important survival behavior that develops later in embryogenesis. Interestingly, previous studies examining the effect of PAHs on zebrafish swimming behavior did not reveal any significant phenotypes [36]. Therefore, we systematically tested whether exposure to Macondo crude oil WAF impacted swimming patterns and escape responses. To do this, we recorded the swimming behavior of individual 48 hpf larvae with a high-speed video camera (1,000 frames/second) following the administration of a specific touch stimulus [60]. WAF-treated embryos demonstrated abnormal swimming behavior and a failure to escape based on multiple criteria. WAF-treated embryos showed reduced sensitivity to touch stimuli, as demonstrated by 70% response rate for WAF-treated embryos as compared to a 99% response rate for untreated control embryos (n = 100 trials from 10 embryos each). When a response was produced in WAF-treated embryos they showed a significantly reduced frequency of body bends (Control, 39.10Hz; WAF, 18.82Hz; n = 10 each; t-test, P < 0.01) and swam for less time than untreated control embryos (Control, 875.8mS; WAF, 282mS; n = 10 each; t-test, P = 0.01) (Figure 6). The presence of locomotor behavior phenotypes suggests that there could either be a problem with neural transmission or a developmental problem resulting from an anatomical deformation in the nervous or musculature systems.

Neuronal development in the central and peripheral nervous system

Development of locomotor movement in response to touch stimuli requires a complex neural network that begins with an elaborate meshwork of Rohon Beard sensory axons at the periphery that originate from the dorsal neural tube. These bipolar sensory neurons make connections with a variety of interneurons that function to relay signals to Mauthner neurons, which serve as the major motor control center in the hindbrain. Mauthner neurons then send signals back down the spinal cord to stimulate coordinated motor neuron activation to achieve the alternating contraction of skeletal muscle required for swimming behaviors [61–63]. In order to determine what underlying developmental processes may be contributing to the visible defects in locomotor behavior, we used specific antibody markers to visualize each cellular step in the locomotor neural circuit.

Anti-Acetylated Tubulin (AT) labels all axonal pathways in the zebrafish as well as specifically marks the somas of Rohon Beard sensory neurons [64]. Anti-Islet-1 labels both the nuclei of Rohon Beard Sensory neurons and motorneurons, anti-Gaba labels a series of interneurons, and the 3A10 antibody marks Mauthner neurons in the hindbrain [65–67]. Surprisingly, using this spectrum of neuronal markers we found only one consistent and specific anatomical deformation that was restricted to the peripheral projections of sensory axons. The Mauthner neurons that serve as the central mediators for startle-reflex behavior in the hindbrain, showed absolutely no difference in number or axonal projections between WAF-treated and untreated control embryos (Figure 7A, B; n = 60) [67–69]. Likewise, no statistical difference was seen in the average number or position of Gaba-positive DoLa, CoSA, VeLD or KA interneurons (Figure 7C, D; Control, 41.1 cells, n = 60; WAF, 41.3 cells, n = 59; t-test, P = 0.855).

Investigation of motorneuron development did not reveal major differences in their cell differentiation. Specifically, anti-AT labeling of primary motor axons did not show consistent defects over the length of the trunk (Figure 7E, F, arrows). It should be noted that while occasional errors in motor axon pathfinding were detected, they were always associated with an affiliated muscle patterning defect that we describe in detail later. Quantification of three separate replicate experiments of Islet1 labeling for primary and secondary motorneurons at 30 hpf showed only minor reductions in the number of motorneurons, with only one of the three replicates actually exhibiting statistical significance (Figure 7G, H, lower bracket; Rep 1: 16% reduction (control n = 11, WAF n = 20), t-test, P = 0.0001; Rep 2: 4.6% reduction (control n = 18, WAF n = 18), Mann-Whitney test, P = 0.456; Rep3: 6.6% reduction (control n = 20, WAF n = 19), Mann-Whitney test, P = 0.043). These results suggest that in some limited way motorneuron number may be impacted by exposure to Macondo oil WAF. However, based on the relatively normal pattern of primary motor axons, very modest overall reductions in number, variable significance and time period of analysis correlating with the middle of secondary motorneuron birth [65], we attribute these minor decreases in motorneuron populations more likely to a mild developmental delay in treated embryos rather than any biologically relevant effect from the oil.

Similarly, no qualitative differences were seen in the position or morphology of Rohon Beard sensory neurons as detected with anti-AT labeling (Figure 7E, F asterisks). Quantification of Rohon Beard sensory neuron numbers with anti-Islet1 showed little to no effect (Figure 7G, H, upper bracket). Similar to motorneurons, only one of the three replicates revealed a statistically significant difference (Rep 1: 2% increase (control n = 11, WAF n = 20), t-test, P = 0.72; Rep 2: 6.3% reduction (control n = 18, WAF n = 18), t-test, P = 0.184; Rep 3: 15.6% reduction (control n = 20, WAF n = 19), t-test, P = 0.0001). Again, based on the normal morphology and position of Rohon Beard cells, with no statistical difference present in the first two replicates, and only a small effect observed in the third replicate, we conclude Rohon Beard sensory neuronal number to be unaffected by Macondo oil. However, analysis of the meshwork of sensory axonal projections in the periphery was consistently both visually and quantitatively significantly reduced (Figure 7I, J, Control axonal labeling intensity = 1274.1 pixels, n = 55; WAF axonal labeling intensity = 883.9 pixels, n = 59; t-test, P = 0.0001). These results suggest most of the anatomical development of the locomotor circuitry is unaffected by Macondo crude oil WAF with the exception of subtle but consistent deformations in the amount and/or branching dynamics of sensory axonal projections.

While the overall number of many key neuronal cell types was normal in WAF-treated embryos, we wanted to confirm that radial glial cells, which serve as the neural stem cell population in the developing spinal cord, were also unaffected [70–72]. Using an antibody to Glial fibrillary acidic protein (Gfap) to mark radial glia we show that radial glial cell staining throughout the spinal cord appeared normal (data not shown). Most relevant was the normal number of Gfap-positive cell somas located at the ventricular surface of the neural tube (Figure 7K, L, arrowheads; Control, 5.99 cells, n = 40; WAF, 5.67 cells, n = 40; t-test, P = 0.582). Anti-Gfap labeling fills radial glial cell bodies when they are undergoing mitosis at the ventricular zone (Johnson and Barresi, in preparation; [73]). Normal numbers of such dividing radial glia indicates that exposure to Macondo crude oil WAF does not affect neural stem cell proliferation during embryogenesis.

Somitogenesis and muscle fiber type development

Because our analysis of the nervous system showed specific deformation restricted to the axonal projections of the peripheral nervous system, it was possible that these defects were secondary to deformations in the paraxial mesodermal environment through which these axonal projections need to navigate. During somite development, radially migrating slow muscle precursor cells provide key guidance cues to the simultaneously outgrowing motor axons [74]. Therefore, any defects in the proper specification, migration and/or position and integrity of slow muscle fibers could influence the development of the peripheral nervous system. We exposed embryos from 3.5 hpf to 48 hpf in Macondo crude oil WAF and assayed for F59 labeling, which preferentially recognizes slow muscle myosin in zebrafish [75, 76]. As with most assays, we discovered embryos displaying a range of slow muscle development phenotypes from no observable defects to the loss of muscle fibers and segment boundary errors. Interestingly, similar to what was observed for our cell death analysis over time, embryos displaying slow muscle phenotypes were extremely severe during initial treatments but these phenotypes decreased significantly over the course of several months of repeated experiments using the same crude oil source for WAF preparation (Figure 8).

Initial experiments in November 2010 showed clear defects that represented several distinguishable phenotypes in the treated embryos (Figure 8A-D). The first was the sporadic instance of defects in proper somite boundary formation, such that a segment boundary in a portion of one somite would be absent as represented by slow muscle fibers extending from the anterior boundary of one somite to the posterior boundary of the neighboring somite (Figure 8B, C, arrowhead). Most interestingly, double labeling for motor axons showed pathfinding errors in the affected somite that were directly correlated to the somite/slow muscle defect (Figure 8B, asterisk, arrow). These results suggest that Macondo crude oil may not only be affecting slow muscle fiber development but also somitogenesis, the process by which segment boundaries are established in the paraxial mesoderm [77–79]. The second distinguishable phenotype was the sporadic loss and disorganization of slow muscle fibers in the superficial monolayer (Figure 8D), which suggests impairments in slow muscle differentiation and subsequent migration in WAF-treated embryos.

Later experiments revealed somitogenesis defects with corresponding motor axon pathfinding errors, but these deformations were not as dramatic as compared to our first experiments (Figure 8E-G) and subsequently absent from the final replicates (Figure 8H-M). Later experimentation still showed extremely sporadic loss and disorganization of the slow muscle monolayer (Figure 8H-M). Interestingly, high resolution imaging of regions showing reductions in slow muscle fibers revealed muscle phenotypes resembling muscle degeneration [80–85]. Variable sized fragments of slow muscle myosin were found present in locations devoid of morphologically normal slow-twitch fibers (Figure 8I, J, red). In contrast to the somite boundary defects, motor axon pathfinding appeared normal in areas showing these missing or degenerating muscle fibers (Figure 8I, J, green). Lastly, these phenotypes continued to diminish in severity upon our last round of treatment (Figure 8K-M).

The sporadic nature of muscle phenotypes both in a clutch of treated embryos and within an affected embryo paired with the gradual loss of these phenotypes over time suggests that the causative agent in the crude oil is not particularly potent and somehow loses its activity over time. Therefore, in an attempt to reproduce the severity of the muscle and somitogenesis defects observed initially, we exposed embryos from 3.5 hpf to 48 hpf in WAF that was refreshed every 15 h. Similar to our results of increased apoptosis in refreshed WAF treatments, more severe muscle deformations were present in refreshed WAF-treated embryos as compared to untreated controls and non-refreshed WAF-treated embryos (Figure 9). The sporadic nature of these deformations was consistent, but the severity was now qualitatively similar to our initial experiments. Remarkably, somitogenesis defects were detected again, showing slow muscle fibers crossing in locations that would normally have a somitic boundary (Figure 9D, D', arrowheads) as well as the presence of irregularly shaped somites (Figure 9D', arrows). In addition, significant slow muscle loss and potential degeneration was also observed following this WAF refreshing protocol. Specifically, slow muscle myosin fibrils were seen in varying stages of degeneration (Figure 9E). This type of dose-response approach confirms that some component(s) within the Macondo crude oil WAF do directly disrupt somitogenesis and slow muscle development.

Discussion

By all standard measures the Deepwater Horizon blowout caused the worst oil spill the Gulf of Mexico has ever experienced, and recent news reports suggest oil might still be leaking from the Macondo well into the Gulf waters [4, 86–89]. To truly assess the total impact of this disaster it will be critical to monitor the fauna and flora of the Gulf of Mexico and Atlantic Ocean for years to come. To make this assessment efficient and thorough, researchers will need to know the range of phenotypes expected from exposure to Macondo oil; however, collecting this information from fish growing within these waters may be particularly challenging. If native species encountered the Macondo oil from the Deepwater Horizon spill during their embryonic or larval stages, these organisms may have died shortly after exposure or were eaten by predators, limiting the number of specimens available for study. Moreover, collection procedures for critical stages of embryonic development and reliable endpoint assays are limited for the analysis of native species from the Gulf of Mexico. In this study we used the tractable zebrafish model system to determine whether water-soluble components of the Macondo oil collected from the riser during the oil spill could directly impact the embryonic development of a bony fish. WAF made from the Macondo oil did not cause wide spread toxicity or even cause significant problems with the earliest developmental processes required by the embryo to progress through cleavage, gastrulation and neurulation. This is surprising, as these early stages of development are arguably the most vulnerable to any environmental teratogen. Rather, our data support a model in which Macondo crude oil WAF cause specific developmental deformations that exhibit both spatial and temporal selectivity.

Many fish species, such as the commercially relevant Atlantic bluefin tuna, red snapper and gag grouper all lay their eggs in the open waters of the Gulf of Mexico near the site of the Deepwater Horizon platform [90–93]. The produced embryos are carried by water currents to the shallows of the Gulf shores to develop into larvae before swimming back into the open ocean as juvenile fry. Unfortunately, the Macondo oil from the Deepwater Horizon disaster was similarly carried along current driven paths to the shores and throughout the Gulf of Mexico [41]. Historically most oil spills have occurred at or near the surface of the water, which would result in limited hydrocarbon dissolution, particularly for more volatile hydrocarbons that are quickly lost to the atmosphere. However, the Deepwater Horizon oil spill is unique in its deep sea origin, which provided the crude oil more time and exposure to the water column creating underwater plumes mostly composed of water-soluble fractions of C₁-C₃ hydrocarbons and aromatic compounds [42, 43]. Therefore, understanding the impact that water accumulated fractions may have on the development of native species is particularly relevant for this disaster. In fact, our results demonstrate that the hydrocarbon concentrations that produced phenotypes in zebrafish embryos are comparable to the levels detected in the underwater plumes [42, 43] and along the Louisiana marshlands that affected gene expression in adult killifish [44]. It is known that interactions between crude oil and various environmental factors, such as temperature, salinity and pressure, will impact hydrocarbon dissolution and PAH uptake [94, 95]; however, while our WAFs were largely made in fresh water, the similar ranges of hydrocarbon concentrations recently documented in the Gulf waters following the spill suggest our experiments can provide real insight into the potential risks faced by native species that spawned in the Gulf of Mexico during and after this oil spill.

We observed three broad phenotypes following treatment with Macondo oil WAF. The first observation was a mild but consistent reduction in embryo size paired with changes in head and trunk morphology, and the second phenotype was a compromised cardiovascular system. Both of these broad effects are consistent with responses reported previously to a variety of crude oil sources and specific PAHs [6]. However, we report here for the first time that the Macondo oil WAF does dramatically reduce touch sensitivity and impair proper swimming behavior. Using a variety of molecular and cellular labeling procedures paired with high resolution microscopy we were able to further elucidate the developmental origins behind these three broad observations.

Defects in size and shape through induction of apoptosis

WAF-treated zebrafish embryos had visible reductions and morphological changes in the size and shape of the head and trunk. These phenotypes could be explained by a reduction in cell proliferation or increase in programmed cell death. We found there was no reduction in the number of mitotic cells (Figure 3A, B), which was further confirmed by no change in the number of dividing neural stem cells (Figure 7K, L). These data suggest cell division rates were unaffected by Macondo crude oil WAF. However, we did detect a statistically significant increase in the amount of apoptosis (Figure 3C-I), supporting a cell death regulatory role for some component in the crude oil. This component could actively induce cell death or play a role in the repression of a survival factor. There are relevant data to support this hypothesis; crude oil, fuel oils, or specific PAHs have been documented to up-regulate known apoptotic proteins in juvenile cod, to increase programmed cell death in cultured dolphin renal cells, and to trigger apoptotic DNA fragmentation in ovarian and liver cells of the juvenile channel catfish [96–98]. We observed an increase in apoptotic cells present inside and outside of the nervous system (Figure 3), suggesting activation of programmed cell death was not necessarily tissue specific. Systematic chemical analysis in zebrafish could help discern which components of the Macondo oil are responsible for induction of programmed cell death and whether induction is cell type specific.

Selective impairment of neural crest cells is at the 'heart' of the problem

While increased cell death may play a role in the defects contributing to reductions in embryo size and shape, reductions in head size may be more directly associated with a lack of proper jaw formation. Defects in craniofacial development in response to crude oil or specific PAHs have been demonstrated previously [36]. The most prevalent and severe craniofacial defect we observed in response to Macondo crude oil WAF was the preferential loss of posterior pharyngeal cartilage elements (Figure 5A-F). As one might expect, the vasculature associated with these same pharyngeal arches was also reduced (Figure 4A-H). Most crude oils, or their components, cause cardiac edema, heart morphogenesis defects, and reduced circulatory function during embryogenesis of several fish species [9, 36, 38, 47]. We hypothesized that the defects we observed in pharyngeal cartilage, vasculature development and heart morphogenesis were linked by an earlier disruption in the proper development of cranial neural crest cells, which are contributing precursors for all of these tissues.

Neural crest cells function as multipotent stem cells that actively delaminate from the dorsal neural tube and migrate along separate pathways across the entire anterior-posterior axis of an organism. During migration to their final destinations neural crest cells differentiate into a variety of cell types, some of which contribute to the development of pigment cells, peripheral nervous system, head cartilage, endothelial and smooth muscle vasculature, and portions of the heart [52–56]. Interestingly, recent investigations in amniotes have suggested pharyngeal arches and the heart are derived from the same "vagal" domain of neural crest cells lying at the intersection between the head and trunk axial positions (reviewed in [52]). This is of particular relevance since the most significant phenotypes we observed were restricted to the pharyngeal arch cartilage, arch vasculature and heart (Figure 4). Importantly, cardiac neural crest cells specifically migrate through the posterior pharyngeal arch pathways on route to the developing heart fields, where they differentiate into smooth muscle and endothelial cell derivatives that contribute to the morphogenesis of the outflow tract, septum, and valves of the heart [51, 55].

We discovered that Macondo WAF-treated embryos show a specific reduction in one of the posterior arches, and a similar restricted reduction was seen in both crestin and dlx2 gene expression by cranial neural crest cells associated with the posterior pharyngeal arches (Figure 5G-P). Initially cranial neural crest cells migrate in three streams toward the presumptive arches, and the posterior-most stream undergoes a branching process to form three additional streams that establish the posterior most pharyngeal arches [99]. Therefore, we hypothesize that the causative toxins in the Macondo WAF may be affecting neural crest cell specification as it relates to their ability to carry out this branching step during posterior pharyngeal arch development. This spatially restricted defect in neural crest development is a remarkably targeted effect by crude oil, which suggests there are equally specific molecular pathways directly influenced by the components of the Macondo WAF; such as, the known neural crest regulators Wnt, Fibroblast growth factor, or the Bone Morphogenic Protein signaling pathway [51, 100, 101]. These pathways may be activated directly or independent of the aryl hydrocarbon receptor 1 and 2, which has been shown to be required for cardiac edema and heart morphogenesis defects in response to selective PAHs [37].

Despite the apparent lack of neural crest defects in the trunk of WAF-treated embryos, there was reduced circulation in the intersegmental blood vessels, and those vessels devoid of any circulation often showed excessive vascular branching (Figure 4L-O'). These elaborate and often forked branching patterns (Figure 4N', O', arrow) were reminiscent of an angiogenic process called intussusception, in which a vessel splits along its longitudinal axis and undergoes vascular remodeling [102, 103]. While intussusception has not yet been described in zebrafish, others have demonstrated mouse retinal vasculature responds to hypoxic conditions by forming characteristic "vascular loops" [104]. In WAF-treated embryos vascular remodeling is seen only in intersegmental blood vessels that are devoid of circulation, which could represent an extreme but focused hypoxic event during which vascular looping might be observed (Figure 4N', bracket). We, therefore, hypothesize that the vascular remodeling observed in WAF-treated embryos is an indirect effect caused by reduced circulation in the intersegmental blood vessels due to a primary disruption in early neural crest-mediated heart development and function.

Defects in patterning the peripheral nervous system impacts locomotor escape behaviors

Like most teleosts, zebrafish larvae evolved early stereotypical swimming patterns in response to touch stimuli that enable fast escape locomotor behaviors [105, 106]. The inability to properly react to touch would have adverse consequences to larva survival. We observed that larvae exposed to the Deepwater Horizon crude oil had significantly reduced sensitivity to touch and disorganized swimming patterns relative to untreated controls (Figure 6). A previous study that examined the effects of specific PAHs on zebrafish locomotor behaviors did not detect any irregularities [36], suggesting that either the Macondo crude oil WAF possesses a unique component or a particularly toxic combination of known components impaired proper locomotor function. This could have unfortunate implications for the species of the Gulf of Mexico and Atlantic Ocean where even subtle reductions in larval or adult escape responses can be deadly. There is some precedent for this, as delayed escape behaviors have been documented in fiddler crabs in response to chronic exposure to No. 2 fuel oil polluting the sediment of Wild Harbor in Buzzards Bay, MA [107]. We sought to determine the developmental origin of the locomotor phenotype in WAF-treated embryos by assessing the anatomical organization of the neural circuitry and skeletal muscle necessary to respond to touch and yield functional swimming behaviors. Considering the complexity of the locomotor system, we were surprised to only detect specific deformations in the peripheral nervous and muscular systems; the neurons and astroglia within the central nervous system were normal in quantity and position (Figures 7, 8).

Similar to our findings of touch response defects, the peripheral sensory and motor axon defects and slow muscle patterning phenotypes, to the best of our knowledge, have never previously been documented. Specifically, Macondo crude oil WAF caused reduced sensory axonal branching along the entire trunk, and sporadic motor axon pathfinding errors directly associated with corresponding deformations in slow muscle fiber development. Reductions in sensory neuronal branches likely cause reductions in touch responses [108, 109], which suggests that WAF-induced reductions in sensory axonal arbors contribute to the reduction in touch sensitivity. However, when a touch response was elicited in a WAF-treated larva, they exhibited disorganized swimming behaviors. While problems in sensory branching may contribute to these swimming errors, the cause is more likely a problem with stimulus transduction controlled by the downstream neural circuitry and muscular output [110].

WAF-treated embryos exhibit deformations in motor axon pathfinding and slow muscle development (Figure 8). These specific defects could definitely lead to impaired muscle contractions and swimming behaviors. Early muscle contractions have been shown to be required for the proper ventral trajectory of pathfinding sensory axons and their ability to exhibit appropriate self-avoidance behaviors to establish the mesh-like pattern of sensory branching [111]. However, this is not likely a significant influence as muscle and motor axon defects were not consistently seen throughout the trunk of WAF-treated embryos unlike the sensory axonal defects, nor were longitudinal pathfinding errors or significant axon to axon contact seen that are characteristically found following muscle contraction loss [111].

Motor axon pathfinding errors were only found in somites that exhibited corresponding slow muscle patterning defects, which strongly suggests motor axon pathfinding errors are not direct effects of the oil but rather indirect phenotypes in response to inappropriate guidance cues derived from earlier problems with somitogenesis and slow muscle patterning. This is in contrast to the sensory neuron branch reductions that are uniformly present throughout the trunk and, thus, likely a direct affect of exposure to the Macondo crude oil. Slow muscle cells have been shown to provide critical axon guidance cues that direct the proper pathfinding of motor axons [74, 112]. This primary defect in early skeletal muscle development can be interpreted as two separable processes, in which there are changes to the highly stereotypical pattern of segmentation and then improper slow muscle positioning.

Within the musculature of the trunk we observed losses of somitic boundaries as well as the occurrence of inappropriate boundaries within the same somitic region (Figure 8B, C, F, G as examples). At this point we can only speculate how Macondo crude oil might be affecting somitogenesis. Segmentation in vertebrates is controlled by the precise coordination of a Notch-Delta mediated molecular clock that determines when a boundary will form and this process is paired with opposing anterior and posterior morphogenic gradients of Retinoic acid and Fibroblast growth factor that define the location of a segment boundary [77, 79, 113–116]. It is possible that some component within the Macondo crude oil might be impacting this somite molecular clock mechanism; however, it is also plausible that our WAF treatments were affecting the terminal step in boundary formation that involves the process of epithelialization and formation of the myotendinous junction rather than the timing of somitogenesis [117, 118].

After a segment boundary has formed in the paraxial mesoderm of zebrafish, "adaxial" slow muscle precursor cells located adjacent to the notochord undergo substantial morphogenesis and movement to the outer-most edge of a somite to form a monolayer of elongated, slow-twitch muscle fibers [76, 119, 120]. While alterations in proper somite boundary formation would yield irregularly elongated slow muscle fibers, it has not been documented to cause alterations in the medial to lateral positioning of fibers, change the parallel positioning of the slow muscle array, nor cause early slow muscle loss [118]. Therefore, we hypothesize that in addition to somite formation defects, Macondo crude oil WAFs may be independently affecting some aspect of slow muscle specification and migration.

Hedgehog signaling is required for proper slow muscle cell specification and Cadherin cell adhesion molecules are required for proper slow muscle morphogenesis and movement, and their loss causes slow muscle positioning phenotypes similar to what we observed following WAF treatments [120–122] (Figure 8D, L, M as examples). While these conclusions related to muscle development are speculative, they provide a basis for a series of future experiments aimed at analyzing the effects of specific Macondo crude oil compounds on somitogenesis and muscle development, as well as examining the role of the Aryl hydrocarbon receptor signaling pathway in these processes [37].

Aside from these early somitogenesis and muscle fiber type patterning defects, a separate and later forming slow muscle degeneration phenotype was also variably present in some WAF-treated embryos. We found a number of embryos treated with the Macondo oil WAF had sporadic muscle fiber breaks and single sided detachment from the lamina, which subsequently exhibited cell death morphologies (Figure 8I, J). We interpret this phenotype as a specific, WAF-mediated muscle degeneration, as it is nearly identical to the muscle pathology seen in zebrafish genetic models of muscular dystrophy [80–85]. Importantly, this late muscle degeneration defect does not have corresponding motor axon pathfinding errors because it occurs after motor axons have already successfully reached their target cells. While these varied early and late muscle phenotypes have real consequences for embryonic health and locomotor function, the sporadic nature of these muscle phenotypes suggests they cannot fully account for the consistent errors in swimming behavior exhibited by WAF-treated embryos.

The abnormal locomotor behaviors exhibited by WAF-treated larvae could be due to defects in central nervous system function. Our level of analysis did not reveal any neuroanatomical defects; however, fine mapping of neural circuits or analysis of neuronal network activity could help elucidate specific cellular and molecular mechanisms disrupted by crude oil exposure. Moreover, it will be equally important to characterize the quality of myelin wrapping by oligodendrocytes and schwann cells, which contribute significantly to how well signals are conducted between neurons.

Phenotypic changes over time

An unexpected finding of our research was the phenotypic reduction in certain defects over successive and identical experimental replicates. Specifically, apoptotic cell death and skeletal muscle phenotypes decreased in severity over the course of multiple experiments, while the phenotypes associated with neural crest development and sensory neuronal branching remained consistent. This observation suggests that different components within the Macondo crude oil might cause these phenotypes, and that some specific component(s) changed over the course of the use and storage of our Macondo crude oil sample. Importantly, we were able to reproduce the severity of both cell death induction and the severity of all the skeletal muscle phenotypes by exposing embryos to freshly mixed WAF preparations several times over the course of a single experiment. This confirms that Macondo crude oil is responsible for these phenotypes and, while the unidentified compound has reduced potency over time, it is still present and capable of impairing embryonic development. A recent study demonstrated that dissolved PAHs, rather than oil particles, are toxic to zebrafish embryos and cause edema, hemorrhaging, developmental delays, and abnormalities in cardiac function [38]. We propose a model in which the more readily dissolved PAHs are responsible for the neural crest derived phenotypes that lead to cardiac and craniofacial deformations, whereas the cell death and skeletal deformations may be caused by novel Macondo oil components, such as smaller ringed hydrocarbons that are more easily released from the WAF as a gas, or much heavier hydrocarbons that readily fall out of solution. Our findings will enable logical candidate approaches to analyze the role of individual components of Macondo oil in regulation of specific developmental processes during fish embryogenesis.

Conclusions

These studies demonstrate that water-soluble components of Macondo crude oil cause specific teratogenic effects on developing zebrafish embryos. While exposure to Macondo oil WAFs did yield similar defects in cardiovascular and craniofacial development as with other crude oil types, we show this is likely due to an earlier impairment in the development of cranial neural crest cells. In addition, irregular locomotor escape responses in Macondo oil WAF treated larvae may be in part due to specific reductions in sensory axon branching as well as deformations in somite and slow muscle development. These results shed new light on a variety of specific developmental processes never before associated with crude oil exposure that provide a framework for future studies to define the molecular mechanisms governing crude oil teratogenesis. These novel phenotypes suggest that Macondo crude oil sampled during the Deepwater Horizon oil spill is toxic to zebrafish embryonic development, and, based on the high conservation of developmental mechanisms Danio rerio shares with other vertebrate species, the Macondo crude oil will similarly impact the embryonic development of native teleost species known to spawn in the Gulf of Mexico. We predict these findings can be used as a guide to initiate more efficient and systematic analyses of native species that may have been impacted by the original Deepwater Horizon oil spill and those species that could be affected by future leakage from the Macondo well.

Methods

Sampled Macondo crude oil

A one-liter sample of Macondo crude oil, MC 252 (Source Oil B; ID #: 20100617-121) from the Deepwater Horizon oil spill was provided by British Petroleum (BP) on September 8, 2010. This oil sample was collected from the riser insertion tube on the Enterprise by Entrix samplers during May 2-3, 2010. BP acknowledged that during sampling of this crude oil, Nalco EC9323A defoamer was being injected topside, while methanol with 10,000 ppm VX9831 oxygen scavenger/catalysts solution was being injected subsea. While the presence of these additional agents in the sample cannot be ruled out, it is unlikely they were incorporated into this crude oil sample due to the method of sampling directly through the riser tube. It was further acknowledged by BP that there was a variable amount of water in the oil samples collected in this manner. Material safety data sheets for the Source Oil B crude oil sample stated its major constituents were n-hexane, toluene, xylene, benzene, naphthalene, ethylbenzene, and hydrogen sulfide.

Water accommodated fraction (WAF)

Following previously accepted mixing procedures, we created water accumulated fractions (WAF) of Macondo oil with autoclaved E3 embryo medium [40, 123]. Specifically, the 1-liter container of Macondo crude oil was slowly inverted 20 times before collecting a sample to ensure consistent sampling over the course of the study. Oil dilutions of 1:10 in embryo medium were prepared in cap-sealed glass bottles that allowed for 20% air volume. Initial gas chromatography mass spectrometry (GCMS) analysis of WAF exposed to plastics detected n-butyl phthalate in solution, which is a plasticizer speculated to cause developmental effects on its own (data not shown, [124]). Therefore, only glass pipettes and glass petri dishes were used with WAF solutions. For initial characterization, WAF stock solutions were mixed with a magnetic stir bar in two different ways: (1) WAF stock was stirred at a slow, non-vortex inducing mixing speed [40]; and (2) WAF stock was stirred at a rate sufficient to produce a vortex equivalent to one-third the volume of the solution. Both solutions were mixed for 24 h, followed by a 2 h resting period before only the aqueous WAF phase was sampled. Unless otherwise noted, the embryos in the following experiments reported here were exposed to a 100% WAF solution derived from the 1:10 (crude oil to embryo media) vortex-mixed stock solution.

WAF chemical analysis

To determine what the chemical composition was of the resulting WAF solutions made in embryo medium, Solid phase microextraction (SPME,100 mm polydimethylsiloxane) and gas chromatography mass spectrometry (GCMS, Agilent 7890A GC/5975C MSD) were performed. WAF samples were analyzed within one hour after the mixing procedure was completed. The SPME fiber was immersed for six minutes in a 15 mL vial of diluted WAF (25-fold dilution), with constant stirring, before insertion into the GC (helium carrier gas; splitless mode for first six minutes; 220°C inlet; oven at 35°C for four minutes, ramped 8°C/minute to 275°C, held at 275°C for three minutes). For consistency among WAF samples, standards for selected components (cyclopentane, methylcyclohexane, n-hexane, n-decane, n-tetradecane, benzene, toluene, xylenes, naphthalene, anthracene, phenanthrene, all from Supelco) were also made in diluted embryo medium (25-fold dilution). Benzene-d6 (Supelco) was added as an internal standard. An expanded explanation of the chemical analysis is provided in Additional files 1 and 2.

Embryo collection and treatment

Fish lines were maintained in the ALAAC accredited Smith College Zebrafish Facility using standard husbandry techniques ([125]; Zebrafish International Resource Center). Fertilized eggs from wild type embryos (AB strain) and Tg[fli:eGfp] transgenic fish (TU/AB background, provided by the Lawson Lab, UMass-Medical School) were collected, washed in embryo medium, and incubated at 28.5°C. Unless otherwise stated, embryos were exposed to WAF solutions starting at 3.5 hours post-fertilization (hpf) and maintained in WAF solutions until a maximum of 5-days post fertilization (dpf). Control embryos were maintained in oil-free embryo medium and grown in a separate 28.5°C incubator to eliminate potential exposure to WAF gases. All treatments were carried out with either 20 mL of solution in 100 mm glass petri dishes or 10 mL of solution in 50 mm glass petri dishes. Prior to fixation or live embryo imaging, embryo chorions were removed by chemical digestion with Pronase (2 mg/ml, Sigma-Aldrich, St Louis, MO, USA) for three to five minutes.

Behavioral analysis

In an effort to perform a more conservative assessment of locomotor behavior, analysis was carried out using a 50% WAF solution. Embryos exposed to either 50% or 100% WAF had similar locomotor responses (data not shown). To characterize larval swimming behavior at 48 hpf, a light touch stimulus was applied to the head of larvae. The minimum stimulus required to elicit a response was determined using pressure-specific Von Frey filaments. The touch-response was recorded using a high-speed camera (Fastec Imaging, San Diego, CA, USA) at 1,000 frames per second (fps). A 35 mm lens (Nikon, Melville, NY, USA) was used for magnification. To illustrate the responses, single frames taken at 20 mS intervals were overlaid in Adobe Photoshop (San Jose, CA, USA).

For kinematic analysis, the head-to-tail angles were calculated for each frame using automated software developed by the Downes Lab (Biology Department, University of Massachusetts, Amherst, MA, USA) [126]. In brief, pixel density was used to identify three landmarks along the larval body: the tip of the nose, the border between the yolk extension, and the tip of the tail. These three points form an angle, which was plotted over time using Microsoft Excel (Microsoft Corporation, Redmond, WA, USA). To calculate body bend frequency, a full body bend was defined as two intervals of more than 50 degrees of opposite directions. To determine the duration of a swimming episode, we measured the beginning of a swimming episode until the final time the body was straightened to within 20 degrees of being straight (defined as 0 degrees).

Blood, circulation and vascular analysis

Visualization of blood in 3 dpf embryos was accomplished by staining hemoglobin with o-Dianisidine as previously described [127]. Blood circulation rates were determined by recording the amount of time a single blood cell took to travel through the dorsal aorta from somite 8 to somite 14. A total of three blood cells were recorded and their travel times averaged for each fish. Individual blood cells were easily visualized in live larvae at 3 dpf using an Olympus stereo microscope (Center Valley, PA, USA).

Microangiography was performed as previously published [49, 128] and described in detail online [129]. Briefly, 3 dpf live control and WAF treated tg[fli:eGfp] larvae were anesthetized with Tricaine (MS222, Argent Chemical Laboratories, Inc, Redmond, WA, USA) to prevent skeletal muscle contractions, mounted ventral side up in 5% methylcellulose, and microinjected with Qtracker 655 non-targeted quantum dots (Invitrogen, Life technologies, Carlsbad, CA, USA) into the sinus venosus. Larvae were then laterally embedded in 0.75% agarose on glass bottom petri dishes (MatTek, Ashland, MA, USA), and imaged with an inverted Leica SP5 Laser Scanning Confocal Microscope (Lieca, Buffalo Grove, IL, USA) with resonant scanning. Live cell imaging of the fluorescently labeled green endothelial cells and red quantum dot-filled vasculature was captured at 20X using bi-directional scanning at 8,000 hz, 16-times line averaging at a 1024 × 1024 resolution, and with a 1.7 × digital zoom. Z-stacks with an optical slice thickness of 1 μm were collected of the entire trunk or portions of the head. Z-stack analysis and maximum intensity projections were performed using Volocity software (PerkinElmer, Waltham, MA, USA). Adobe Photoshop was used to align projections and reconstruct the entire trunk vasculature of individual larva as illustrated in Figure 4L-O.

Immunohistochemistry and imaging

Embryos were fixed in 4% phosphate-buffered formaldehyde, except for anti-Islet1 labeling, which were fixed in 4% formaldehyde, 0.05% glutaraldehyde, 5 μM EGTA, 5 μM MgSO₄ and 0.1% Triton-X-100. Primary antibodies used were mouse IgG_2b anti-Acetylated Tubulin (AT, 1:800; Sigma); rabbit anti-Glial fibrillary acidic protein (Gfap, 1:500; Dako, Carpinteria, CA, USA), mouse IgG₁ anti-Phospho-Histone H3 (PH3, 1:1000, Cell Signaling Technology, Inc., Danvers, MA USA), mouse IgG₁ anti-slow muscle myosin (F59, 1:10; Developmental Studies Hybridoma Bank, University of Iowa, Department of Biology, Iowa City, Iowa, USA), rabbit anti-Gamma-aminobutyric acid (Gaba, 1:1000; Sigma), mouse IgG₁ anti-3A10 (1:50, Developmental Studies Hybridoma Bank), and rabbit anti-activated Caspase 3 (1:500; BD Pharmigen, San Jose, CA, USA). All primary antibodies were diluted in blocking solution (see below). Secondary antibodies used were Alexa-594 goat anti-rabbit IgG, AlexaFluor-594 goat anti-mouse IgG₁, AlexaFluor-647 goat anti-mouse IgG_2b, and AlexaFluor-488 goat anti-mouse IgG₁, all obtained from Invitrogen and diluted 1:200 in blocking solution. Immunocytochemistry was carried out as previously described [130] with minor modifications. Embryos were first dehydrated at -20°C for 20 minutes with 100% MeOH followed by 7 minutes with 100% Acetone. Further antibody penetration was achieved with protein digestion using Proteinase-K (10 μg/ml) for 2 minutes to 25 minutes depending on the age of the embryos. Embryos were incubated in blocking solution (0.5 g BSA; 25 ml Phosphate buffered saline, 0.1% Triton-X-100; 5% normal goat serum; 1% DMSO) prior to both primary and secondary antibody application.

Fluorescent, whole-mount images of fixed preparations were captured using the Zeiss AxioImager epifluorescent compound microscope with ApoTome for structural illumination. Embryos were dissected into separate trunk and head segments. Trunks were laterally mounted on a microscope slide, while heads for 3A10-labeled embryos were mounted dorsal side up. Imaging was performed with either 40× or 20× objectives and Z-stacks were collected with an averaging of 2 and 0.53 μm or 0.8 μm optical slice distance, respectively. An AxioCam Mrc (Carl Zeiss, Thornwood, NY, USA) was used to capture images on the AxioImager, and processing of Z-stacks and maximum intensity projections was done using Axiovision software (Carl Zeiss, Thornwood, NY, USA).

Whole-mount in situ hybridization at for crestin and dlx2 mRNA expression was completed as previously described [131]. Alcian Blue staining was performed to visualize cartilage development at 4 dpf and conducted as previously described [50]. crestin, dlx2, tg(fli:Gfp) labeled pharyngeal arches and Alcian Blue labeling were imaged on a Zeiss Lumar stereo microscope using an AxioCam HR and Axiovision software.

All figures were constructed using Adobe Photoshop. Any adjustments to image brightness, contrast or other properties were done to the entire image and identically performed between controls and WAF-treated data.

Quantitation and statistics

Data collection was obtained in at least 20 embryos per 3 separate replicate experiments for all analyses. One exception was made for the microangiography live embryo imaging where labor intensive microinjection and live embryo mounting restricted analysis to 10 embryos per control and WAF-treated for each replicate. However, at least eight separate locations were imaged along the anterior to posterior axis of each embryo. Cell counts for PH3, Caspase, Gaba, Islet1, and Gfap were done on maximum intensity projections and quantified using the "counting tool" in Adobe Photoshop CS Extended version. Sensory neuron processes were quantified in Image J [132]. Briefly, 8-bit images were converted into binary images to calculate pixel density, and the average number of pixels for each group was analyzed for statistical significance. The results for each replicate were pooled and means calculated for most statistical analyses except where noted in the results. The two-sample T-Test was used to compare treatments with a stringency of P < 0.01 for all analyses, except when the data did not fit a normal distribution, in which case a non-parametric analysis (Kruskal-Wallis or Mann-Whitney tests) was performed. Statistical significance for fli:Gfp labeled arch formation and dlx2 expression was determined using a Fisher's Exact Test.

Authors' information

MB, the corresponding author, is a neurodevelopmental biologist serving as an assistant professor in the Biological Sciences department and member of the Neuroscience program at Smith College.

Abbreviations

AT:: Acetylated Tubulin
BP:: British Petroleum
dpf:: days post-fertilization
fps:: frames per second
Gaba:: Gamma-aminobutyric acid
GCMS:: gas chromatography mass spectrometry
Gfap:: Glial fibrillary acidic protein
hpf:: hours post-fertilization
NOAA:: National Oceanic and Atmospheric Administration
PAH:: polycyclic aromatic hydrocarbons
PH3:: Phosphorylated Histone H3
SPME:: solid phase microextraction
WAF:: water accumulated fraction.

References

1.
Machlis GE, McNutt MK: Disasters. Scenario-building for the Deepwater Horizon oil spill. Science. 2010, 329: 1018-1019.
PubMed CAS Google Scholar
2.
Crone TJ, Tolstoy M: Magnitude of the 2010 Gulf of Mexico oil leak. Science. 2010, 330: 634-
PubMed CAS Google Scholar
3.
Mascarelli A: Deepwater Horizon: after the oil. Nature. 2010, 467: 22-24.
PubMed CAS Google Scholar
4.
Schrope M: Oil spill: deep wounds. Nature. 2011, 472: 152-154.
PubMed CAS Google Scholar
5.
Williams RG, Bejder L, Calambokidis J, Kraus SD, Lusseau D, Read AJ, Robbins J: Underestimating the damage: interpreting cetacean carcass recoveries in the context of the Deepwater Horizon/BP incident. Conser Lett. 2011, 4: 228-233.
Google Scholar
6.
Incardona JP, Collier TK, Scholz NL: Oil spills and fish health: exposing the heart of the matter. J Expo Sci Environ Epidemiol. 2011, 21: 3-4.
PubMed CAS Google Scholar
7.
National Oceanic and Atmospheric Administration, Wildlife reports: Deepwater Horizon Archive. Accessed 12-18-11, [http://www.noaa.gov/deepwaterhorizon/wildlife/index.html]
8.
Richards WJ, McGowan MF, Leming T, Lamkin JT, Kelley S: Larval fish assemblages at the loop current boundary in the Gulg-of-Mexico. Bull Mar Sci. 1993, 53: 475-537.
Google Scholar
9.
Incardona JP, Carls MG, Day HL, Sloan CA, Bolton JL, Collier TK, Scholz NL: Cardiac arrhythmia is the primary response of embryonic Pacific herring (Clupea pallasi) exposed to crude oil during weathering. Environ Sci Technol. 2009, 43: 201-207.
PubMed CAS Google Scholar
10.
Anderson BS, Arenella-Parkerson D, Phillips BM, Tjeerdema RS, Crane D: Preliminary investigation of the effects of dispersed Prudhoe Bay Crude Oil on developing topsmelt embryos, Atherinops affinis. Environ Pollut. 2009, 157: 1058-1061.
PubMed CAS Google Scholar
11.
Pollino CA, Holdway DA: Toxicity testing of crude oil and related compounds using early life stages of the crimson-spotted rainbowfish (Melanotaenia fluviatilis). Ecotoxicol Environ Saf. 2002, 52: 180-189.
PubMed CAS Google Scholar
12.
Lieschke GJ, Currie PD: Animal models of human disease: zebrafish swim into view. Nat Rev Genet. 2007, 8: 353-367.
PubMed CAS Google Scholar
13.
Dahm R, Geisler R: Learning from small fry: the zebrafish as a genetic model organism for aquaculture fish species. Mar Biotechnol (NY). 2006, 8: 329-345.
CAS Google Scholar
14.
Lee HY, Inselman AL, Kanungo J, Hansen DK: Alternative models in developmental toxicology. Syst Biol Reprod Med. 2012, 58: 10-22.
PubMed CAS Google Scholar
15.
Sipes NS, Padilla S, Knudsen TB: Zebrafish: as an integrative model for twenty-first century toxicity testing. Birth Defects Res C Embryo Today. 2011, 93: 256-267.
PubMed CAS Google Scholar
16.
McCollum CW, Ducharme NA, Bondesson M, Gustafsson JA: Developmental toxicity screening in zebrafish. Birth Defects Res C Embryo Today. 2011, 93: 67-114.
PubMed CAS Google Scholar
17.
Yang L, Ho NY, Alshut R, Legradi J, Weiss C, Reischl M, Mikut R, Liebel U, Muller F, Strahle U: Zebrafish embryos as models for embryotoxic and teratological effects of chemicals. Reprod Toxicol. 2009, 28: 245-253.
PubMed CAS Google Scholar
18.
Hill AJ, Teraoka H, Heideman W, Peterson RE: Zebrafish as a model vertebrate for investigating chemical toxicity. Toxicol Sci. 2005, 86: 6-19.
PubMed CAS Google Scholar
19.
Alsop D, Wood CM: Metal uptake and acute toxicity in zebrafish: common mechanisms across multiple metals. Aquat Toxicol. 2011, 105: 385-393.
PubMed CAS Google Scholar
20.
Asharani PV, Lianwu Y, Gong Z, Valiyaveettil S: Comparison of the toxicity of silver, gold and platinum nanoparticles in developing zebrafish embryos. Nanotoxicology. 2011, 5: 43-54.
PubMed CAS Google Scholar
21.
Lanham KA, Prasch AL, Weina KM, Peterson RE, Heideman W: A dominant negative zebrafish ahr2 partially protects developing zebrafish from dioxin toxicity. PLoS ONE. 2011, 6: e28020-
PubMed CAS PubMed Central Google Scholar
22.
Teraoka H, Ogawa A, Kubota A, Stegeman JJ, Peterson RE, Hiraga T: Malformation of certain brain blood vessels caused by TCDD activation of Ahr2/Arnt1 signaling in developing zebrafish. Aquat Toxicol. 2010, 99: 241-247.
PubMed CAS PubMed Central Google Scholar
23.
Prasch AL, Tanguay RL, Mehta V, Heideman W, Peterson RE: Identification of zebrafish ARNT1 homologs: 2,3,7,8-tetrachlorodibenzo-p-dioxin toxicity in the developing zebrafish requires ARNT1. Mol Pharmacol. 2006, 69: 776-787.
PubMed CAS Google Scholar
24.
Carney SA, Peterson RE, Heideman W: 2,3,7,8-Tetrachlorodibenzo-p-dioxin activation of the aryl hydrocarbon receptor/aryl hydrocarbon receptor nuclear translocator pathway causes developmental toxicity through a CYP1A-independent mechanism in zebrafish. Mol Pharmacol. 2004, 66: 512-521.
PubMed CAS Google Scholar
25.
Andreu-Sanchez O, Paraiba LC, Jonsson CM, Carrasco JM: Acute toxicity and bioconcentration of fungicide tebuconazole in zebrafish (Danio rerio). Environ Toxicol. 2012, 27: 109-116.
PubMed CAS Google Scholar
26.
Tierney KB, Sekela MA, Cobbler CE, Xhabija B, Gledhill M, Ananvoranich S, Zielinski BS: Evidence for behavioral preference toward environmental concentrations of urban-use herbicides in a model adult fish. Environ Toxicol Chem. 2011, 30: 2046-2054.
PubMed CAS Google Scholar
27.
Jin Y, Chen R, Sun L, Qian H, Liu W, Fu Z: Induction of estrogen-responsive gene transcription in the embryo, larval, juvenile and adult life stages of zebrafish as biomarkers of short-term exposure to endocrine disrupting chemicals. Comp Biochem Physiol C Toxicol Pharmacol. 2009, 150: 414-420.
PubMed Google Scholar
28.
Sun L, Wen L, Shao X, Qian H, Jin Y, Liu W, Fu Z: Screening of chemicals with anti-estrogenic activity using in vitro and in vivo vitellogenin induction responses in zebrafish (Danio rerio). Chemosphere. 2010, 78: 793-799.
PubMed CAS Google Scholar
29.
Cowden J, Padnos B, Hunter D, Macphail R, Jensen K, Padilla S: Developmental exposure to valproate and ethanol alters locomotor activity and retino-tectal projection area in zebrafish embryos. Reprod Toxicol. 2012, 33: 165-173.
PubMed CAS Google Scholar
30.
Tanguay RL, Reimers MJ: Analysis of ethanol developmental toxicity in zebrafish. Methods Mol Biol. 2008, 447: 63-74.
PubMed CAS Google Scholar
31.
Reimers MJ, Flockton AR, Tanguay RL: Ethanol- and acetaldehyde-mediated developmental toxicity in zebrafish. Neurotoxicol Teratol. 2004, 26: 769-781.
PubMed CAS Google Scholar
32.
Lewis TJ: Toxicity and cytopathogenic properties toward human melanoma cells of activated cancer therapeutics in zebra fish. Integr Cancer Ther. 2010, 9: 84-92.
PubMed Google Scholar
33.
Mizgirev IV, Revskoy S: A new zebrafish model for experimental leukemia therapy. Cancer Biol Ther. 2010, 9: 895-902.
PubMed CAS Google Scholar
34.
Khan T, Benaich N, Malone CF, Bernardos RL, Russell AR, Barresi MJ, Downes GB, Hutson LD: Chemotherapy drugs cause axon outgrowth and behavioral defects in larval zebrafish. J Peripheral Nervous Syst. 2012, 17: 76-89.
CAS Google Scholar
35.
Lessman CA: The developing zebrafish (Danio rerio): a vertebrate model for high-throughput screening of chemical libraries. Birth Defects Res C Embryo Today. 2011, 93: 268-280.
PubMed CAS Google Scholar
36.
Incardona JP, Collier TK, Scholz NL: Defects in cardiac function precede morphological abnormalities in fish embryos exposed to polycyclic aromatic hydrocarbons. Toxicol Appl Pharmacol. 2004, 196: 191-205.
PubMed CAS Google Scholar
37.
Incardona JP, Carls MG, Teraoka H, Sloan CA, Collier TK, Scholz NL: Aryl hydrocarbon receptor-independent toxicity of weathered crude oil during fish development. Environ Health Perspect. 2005, 113: 1755-1762.
PubMed CAS PubMed Central Google Scholar
38.
Carls MG, Holland L, Larsen M, Collier TK, Scholz NL, Incardona JP: Fish embryos are damaged by dissolved PAHs, not oil particles. Aquat Toxicol. 2008, 88: 121-127.
PubMed CAS Google Scholar
39.
Pauka LM, Maceno M, Rossi SC, Silva de Assis HC: Embryotoxicity and biotransformation responses in zebrafish exposed to water-soluble fraction of crude oil. Bull Environ Contam Toxicol. 2011, 86: 389-393.
PubMed CAS Google Scholar
40.
Singer MM, Aurand D, Bragin GE, Clark JR, Coelho GM, Sowby ML, Tjeerdema RS: Standardization of the Preparation and Quantitation of Water-accommodated Fractions of Petroleum for Toxicity Testing. Mar Pollut Bull. 2000, 40: 1007-1016.
CAS Google Scholar
41.
Camilli R, Reddy CM, Yoerger DR, Van Mooy BA, Jakuba MV, Kinsey JC, McIntyre CP, Sylva SP, Maloney JV: Tracking hydrocarbon plume transport and biodegradation at Deepwater Horizon. Science. 2010, 330: 201-204.
PubMed CAS Google Scholar
42.
Reddy CM, Arey JS, Seewald JS, Sylva SP, Lemkau KL, Nelson RK, Carmichael CA, McIntyre CP, Fenwick J, Ventura GT, Van Mooy BA, Camilli R: Composition and fate of gas and oil released to the water column during the Deepwater Horizon oil spill. Proc Natl Acad Sci USA. 2012,
Google Scholar
43.
Ryerson TB, Camilli R, Kessler JD, Kujawinski EB, Reddy CM, Valentine DL, Atlas E, Blake DR, de Gouw J, Meinardi S, Parrish DD, Peischl J, Seewald JS, Warneke C: Chemical data quantify Deepwater Horizon hydrocarbon flow rate and environmental distribution. Proc Natl Acad Sci USA. 2012,
Google Scholar
44.
Whitehead A, Dubansky B, Bodinier C, Garcia TI, Miles S, Pilley C, Raghunathan V, Roach JL, Walker N, Walter RB, Rice CD, Galvez F: Genomic and physiological footprint of the Deepwater Horizon oil spill on resident marsh fishes. Proc Natl Acad Sci USA. 2011,
Google Scholar
45.
Hendzel MJ, Wei Y, Mancini MA, Van Hooser A, Ranalli T, Brinkley BR, Bazett-Jones DP, Allis CD: Mitosis-specific phosphorylation of histone H3 initiates primarily within pericentromeric heterochromatin during G2 and spreads in an ordered fashion coincident with mitotic chromosome condensation. Chromosoma. 1997, 106: 348-360.
PubMed CAS Google Scholar
46.
Vaux DL, Korsmeyer SJ: Cell death in development. Cell. 1999, 96: 245-254.
PubMed CAS Google Scholar
47.
Hatlen K, Sloan CA, Burrows DG, Collier TK, Scholz NL, Incardona JP: Natural sunlight and residual fuel oils are an acutely lethal combination for fish embryos. Aquat Toxicol. 2010, 99: 56-64.
PubMed CAS Google Scholar
48.
Hicken CE, Linbo TL, Baldwin DH, Willis ML, Myers MS, Holland L, Larsen M, Stekoll MS, Rice SD, Collier TK, Scholz NL, Incardona JP: Sublethal exposure to crude oil during embryonic development alters cardiac morphology and reduces aerobic capacity in adult fish. Proc Natl Acad Sci USA. 2011, 108: 7086-7090.
PubMed CAS PubMed Central Google Scholar
49.
Isogai S, Horiguchi M, Weinstein BM: The vascular anatomy of the developing zebrafish: an atlas of embryonic and early larval development. Dev Biol. 2001, 230: 278-301.
PubMed CAS Google Scholar
50.
Javidan Y, Schilling TF: Development of cartilage and bone. Methods Cell Biol. 2004, 76: 415-436.
PubMed Google Scholar
51.
Vincent SD, Buckingham ME: How to make a heart: the origin and regulation of cardiac progenitor cells. Curr Top Dev Biol. 2010, 90: 1-41.
PubMed Google Scholar
52.
Kuo BR, Erickson CA: Regional differences in neural crest morphogenesis. Cell Adh Migr. 2010, 4: 567-585.
PubMed PubMed Central Google Scholar
53.
Kirby ML, Hutson MR: Factors controlling cardiac neural crest cell migration. Cell Adh Migr. 2010, 4: 609-621.
PubMed PubMed Central Google Scholar
54.
Scholl AM, Kirby ML: Signals controlling neural crest contributions to the heart. Wiley Interdiscip Rev Syst Biol Med. 2009, 1: 220-227.
PubMed CAS PubMed Central Google Scholar
55.
Hutson MR, Kirby ML: Model systems for the study of heart development and disease. Cardiac neural crest and conotruncal malformations. Semin Cell Dev Biol. 2007, 18: 101-110.
PubMed CAS PubMed Central Google Scholar
56.
Knight RD, Schilling TF: Cranial neural crest and development of the head skeleton. Adv Exp Med Biol. 2006, 589: 120-133.
PubMed CAS Google Scholar
57.
Luo R, An M, Arduini BL, Henion PD: Specific pan-neural crest expression of zebrafish Crestin throughout embryonic development. Dev Dyn. 2001, 220: 169-174.
PubMed CAS Google Scholar
58.
Akimenko MA, Ekker M, Wegner J, Lin W, Westerfield M: Combinatorial expression of three zebrafish genes related to distal-less: part of a homeobox gene code for the head. J Neurosci. 1994, 14: 3475-3486.
PubMed CAS Google Scholar
59.
Ellies DL, Langille RM, Martin CC, Akimenko MA, Ekker M: Specific craniofacial cartilage dysmorphogenesis coincides with a loss of dlx gene expression in retinoic acid-treated zebrafish embryos. Mech Dev. 1997, 61: 23-36.
PubMed CAS Google Scholar
60.
Burgess HA, Granato M: Sensorimotor gating in larval zebrafish. J Neurosci. 2007, 27: 4984-4994.
PubMed CAS Google Scholar
61.
Clarke JD, Roberts A: Interneurones in the Xenopus embryo spinal cord: sensory excitation and activity during swimming. J Physiol. 1984, 354: 345-362.
PubMed CAS PubMed Central Google Scholar
62.
Clarke JD, Hayes BP, Hunt SP, Roberts A: Sensory physiology, anatomy and immunohistochemistry of Rohon-Beard neurones in embryos of Xenopus laevis. J Physiol. 1984, 348: 511-525.
PubMed CAS PubMed Central Google Scholar
63.
Sagasti A, Guido MR, Raible DW, Schier AF: Repulsive interactions shape the morphologies and functional arrangement of zebrafish peripheral sensory arbors. Curr Biol. 2005, 15: 804-814.
PubMed CAS Google Scholar
64.
Chitnis AB, Kuwada JY: Axonogenesis in the brain of zebrafish embryos. J Neurosci. 1990, 10: 1892-1905.
PubMed CAS Google Scholar
65.
Segawa H, Miyashita T, Hirate Y, Higashijima S, Chino N, Uyemura K, Kikuchi Y, Okamoto H: Functional repression of Islet-2 by disruption of complex with Ldb impairs peripheral axonal outgrowth in embryonic zebrafish. Neuron. 2001, 30: 423-436.
PubMed CAS Google Scholar
66.
Bernhardt RR, Patel CK, Wilson SW, Kuwada JY: Axonal trajectories and distribution of GABAergic spinal neurons in wildtype and mutant zebrafish lacking floor plate cells. J Comp Neurol. 1992, 326: 263-272.
PubMed CAS Google Scholar
67.
Kimmel CB, Sessions SK, Kimmel RJ: Morphogenesis and synaptogenesis of the zebrafish Mauthner neuron. J Comp Neurol. 1981, 198: 101-120.
PubMed CAS Google Scholar
68.
Eaton RC, Farley RD: Development of the Mauthner neurons in embryos and larvae of zebrafish, Brachydanio rerio. Copeia. 1973, 1973: 673-682.
Google Scholar
69.
Prugh JI, Kimmel CB, Metcalfe WK: Noninvasive recording of the Mauthner neurone action potential in larval zebrafish. J Exp Biol. 1982, 101: 83-92.
PubMed CAS Google Scholar
70.
Kriegstein A, Alvarez-Buylla A: The glial nature of embryonic and adult neural stem cells. Annu Rev Neurosci. 2009, 32: 149-184.
PubMed CAS PubMed Central Google Scholar
71.
Park HC, Shin J, Roberts RK, Appel B: An olig2 reporter gene marks oligodendrocyte precursors in the postembryonic spinal cord of zebrafish. Dev Dyn. 2007, 236: 3402-3407.
PubMed CAS Google Scholar
72.
Alexandre P, Reugels AM, Barker D, Blanc E, Clarke JD: Neurons derive from the more apical daughter in asymmetric divisions in the zebrafish neural tube. Nat Neurosci. 2010, 13: 673-679.
PubMed CAS Google Scholar
73.
Leung L, Klopper AV, Grill SW, Harris WA, Norden C: Apical migration of nuclei during G2 is a prerequisite for all nuclear motion in zebrafish neuroepithelia. Development. 2011, 138: 5003-5013.
PubMed CAS PubMed Central Google Scholar
74.
Zeller J, Granato M: The zebrafish diwanka gene controls an early step of motor growth cone migration. Development. 1999, 126: 3461-3472.
PubMed CAS Google Scholar
75.
Crow MT, Stockdale FE: Myosin expression and specialization among the earliest muscle fibers of the developing avian limb. Dev Biol. 1986, 113: 238-254.
PubMed CAS Google Scholar
76.
Devoto SH, Melancon E, Eisen JS, Westerfield M: Identification of separate slow and fast muscle precursor cells in vivo, prior to somite formation. Development. 1996, 122: 3371-3380.
PubMed CAS Google Scholar
77.
Mallo M, Vinagre T, Carapuco M: The road to the vertebral formula. The Int J Dev Biol. 2009, 53: 1469-1481.
PubMed CAS Google Scholar
78.
Shifley ET, Cole SE: The vertebrate segmentation clock and its role in skeletal birth defects. Birth Defects Res C Embryo Today. 2007, 81: 121-133.
PubMed CAS Google Scholar
79.
Mara A, Holley SA: Oscillators and the emergence of tissue organization during zebrafish somitogenesis. Trends Cell Biol. 2007, 17: 593-599.
PubMed CAS Google Scholar
80.
Berger J, Berger S, Hall TE, Lieschke GJ, Currie PD: Dystrophin-deficient zebrafish feature aspects of the Duchenne muscular dystrophy pathology. Neuromuscul Disord. 2010, 20: 826-832.
PubMed Google Scholar
81.
Jacoby AS, Busch-Nentwich E, Bryson-Richardson RJ, Hall TE, Berger J, Berger S, Sonntag C, Sachs C, Geisler R, Stemple DL, Currie PD: The zebrafish dystrophic mutant softy maintains muscle fibre viability despite basement membrane rupture and muscle detachment. Development. 2009, 136: 3367-3376.
PubMed CAS PubMed Central Google Scholar
82.
Hall TE, Bryson-Richardson RJ, Berger S, Jacoby AS, Cole NJ, Hollway GE, Berger J, Currie PD: The zebrafish candyfloss mutant implicates extracellular matrix adhesion failure in laminin alpha2-deficient congenital muscular dystrophy. Proc Natl Acad Sci USA. 2007, 104: 7092-7097.
PubMed CAS PubMed Central Google Scholar
83.
Bassett D, Currie PD: Identification of a zebrafish model of muscular dystrophy. Clin Exp Pharmacol Physiol. 2004, 31: 537-540.
PubMed CAS Google Scholar
84.
Bassett DI, Currie PD: The zebrafish as a model for muscular dystrophy and congenital myopathy. Hum MolGenet. 2003, 12: R265-270.
CAS Google Scholar
85.
Bassett DI, Bryson-Richardson RJ, Daggett DF, Gautier P, Keenan DG, Currie PD: Dystrophin is required for the formation of stable muscle attachments in the zebrafish embryo. Development. 2003, 130: 5851-5860.
PubMed CAS Google Scholar
86.
Walker B: Deepwater horizon oil spill. J Environ Health. 2010, 73: 49-
PubMed Google Scholar
87.
Kerr R, Kintisch E, Stokstad E: Gulf oil spill. Will Deepwater Horizon set a new standard for catastrophe?. Science. 2010, 328: 674-675.
PubMed CAS Google Scholar
88.
Raines B: Deepwater trouble on the horizon: oil discovered floating near source of Mexico spill. alcom. 2011, [http://blog.al.com/live/2011/08/deepwater_trouble_on_the_horiz.html]
Google Scholar
89.
Raines B: Scientists: Oil fouling Gulf matches Deepwater Horizon well. alcom. 2011, [http://blog.al.com/live/2011/08/scientists_oil_fouling_gulf_co.html]
Google Scholar
90.
Block BA, Teo SL, Walli A, Boustany A, Stokesbury MJ, Farwell CJ, Weng KC, Dewar H, Williams TD: Electronic tagging and population structure of Atlantic bluefin tuna. Nature. 2005, 434: 1121-1127.
PubMed CAS Google Scholar
91.
Nelson RS, Manooch CS: Growth and mortality of red snappers in the west-central Atlantic Ocean and northern Gulf of Mexico. Trans Am Fish Soc. 1982, 111: 465-475.
Google Scholar
92.
SEDAR SD, Assessment, and Review: Gulf of Mexico Gag Grouper. SEDAR 10: Stock Assessment Report 2. 2006, Charleston, SC: NOAA, National Oceanic and Atmospheric Administration
Google Scholar
93.
Campagna C, Short FT, Polidoro BA, Mcmanus R, Collette BB, Pilcher NJ, Sadovy De Mitcheson Y, Stuart SN, Carpenter KE: Gulf of Mexico oil blowout increases risks to globally threatened species. BioScience. 2011, 61: 393-397.
Google Scholar
94.
Ramachandran SD, Sweezey MJ, Hodson PV, Boudreau M, Courtenay SC, Lee K, King T, Dixon JA: Influence of salinity and fish species on PAH uptake from dispersed crude oil. Mar Pollut Bull. 2006, 52: 1182-1189.
PubMed CAS Google Scholar
95.
Haftka JJ, Govers HA, Parsons JR: Influence of temperature and origin of dissolved organic matter on the partitioning behavior of polycyclic aromatic hydrocarbons. Environ Sci Pollut Res Int. 2010, 17: 1070-1079.
PubMed CAS Google Scholar
96.
Bohne-Kjersem A, Skadsheim A, Goksoyr A, Grosvik BE: Candidate biomarker discovery in plasma of juvenile cod (Gadus morhua) exposed to crude North Sea oil, alkyl phenols and polycyclic aromatic hydrocarbons (PAHs). Mar Environ Res. 2009, 68: 268-277.
PubMed CAS Google Scholar
97.
Pfeiffer CJ, Sharova LV, Gray L: Functional and ultrastructural cell pathology induced by fuel oil in cultured dolphin renal cells. Ecotoxicol Environ Saf. 2000, 47: 210-217.
PubMed CAS Google Scholar
98.
Weber LP, Janz DM: Effect of beta-naphthoflavone and dimethylbenz[a]anthracene on apoptosis and HSP70 expression in juvenile channel catfish (Ictalurus punctatus) ovary. Aquat Toxicol. 2001, 54: 39-50.
PubMed CAS Google Scholar
99.
Kimmel CB, Miller CT, Keynes RJ: Neural crest patterning and the evolution of the jaw. J Anat. 2001, 199: 105-120.
PubMed CAS Google Scholar
100.
Basch ML, Bronner-Fraser M: Neural crest inducing signals. AdvExp Med Biol. 2006, 589: 24-31.
CAS Google Scholar
101.
Raible DW, Ragland JW: Reiterated Wnt and BMP signals in neural crest development. Semin Cell Dev Biol. 2005, 16: 673-682.
PubMed CAS Google Scholar
102.
Ellertsdottir E, Lenard A, Blum Y, Krudewig A, Herwig L, Affolter M, Belting HG: Vascular morphogenesis in the zebrafish embryo. Dev Biol. 2010, 341: 56-65.
PubMed CAS Google Scholar
103.
Makanya AN, Hlushchuk R, Djonov VG: Intussusceptive angiogenesis and its role in vascular morphogenesis, patterning, and remodeling. Angiogenesis. 2009, 12: 113-123.
PubMed CAS Google Scholar
104.
Taylor AC, Seltz LM, Yates PA, Peirce SM: Chronic whole-body hypoxia induces intussusceptive angiogenesis and microvascular remodeling in the mouse retina. Microvasc Res. 2010, 79: 93-101.
PubMed CAS PubMed Central Google Scholar
105.
Fetcho JR, McLean DL: Some principles of organization of spinal neurons underlying locomotion in zebrafish and their implications. Ann N Y Acad Sci. 2010, 1198: 94-104.
PubMed PubMed Central Google Scholar
106.
Brustein E, Saint-Amant L, Buss RR, Chong M, McDearmid JR, Drapeau P: Steps during the development of the zebrafish locomotor network. J Physiol, Paris. 2003, 97: 77-86.
Google Scholar
107.
Culbertson JB, Valiela I, Peacock EE, Reddy CM, Carter A, VanderKruik R: Long-term biological effects of petroleum residues on fiddler crabs in salt marshes. Mar Pollut Bull. 2007, 54: 955-962.
PubMed CAS Google Scholar
108.
Issa FA, O'Brien G, Kettunen P, Sagasti A, Glanzman DL, Papazian DM: Neural circuit activity in freely behaving zebrafish (Danio rerio). J Exp Biol. 2011, 214: 1028-1038.
PubMed PubMed Central Google Scholar
109.
Svoboda KR, Linares AE, Ribera AB: Activity regulates programmed cell death of zebrafish Rohon-Beard neurons. Development. 2001, 128: 3511-3520.
PubMed CAS Google Scholar
110.
Ribera AB, Nusslein-Volhard C: Zebrafish touch-insensitive mutants reveal an essential role for the developmental regulation of sodium current. J Neurosci. 1998, 18: 9181-9191.
PubMed CAS Google Scholar
111.
Paulus JD, Willer GB, Willer JR, Gregg RG, Halloran MC: Muscle contractions guide rohon-beard peripheral sensory axons. J Neurosci. 2009, 29: 13190-13201.
PubMed CAS PubMed Central Google Scholar
112.
Beattie CE, Granato M, Kuwada JY: Cellular, genetic and molecular mechanisms of axonal guidance in the zebrafish. Results Probl Cell Differ. 2002, 40: 252-269.
PubMed CAS Google Scholar
113.
Holley SA: The genetics and embryology of zebrafish metamerism. Dev Dyn. 2007, 236: 1422-1449.
PubMed CAS Google Scholar
114.
Cinquin O: Understanding the somitogenesis clock: what's missing?. Mechan Dev. 2007, 124: 501-517.
CAS Google Scholar
115.
Baker RE, Schnell S, Maini PK: A clock and wavefront mechanism for somite formation. Dev Biol. 2006, 293: 116-126.
PubMed CAS Google Scholar
116.
Stickney HL, Barresi MJ, Devoto SH: Somite development in zebrafish. Dev Dyn. 2000, 219: 287-303.
PubMed CAS Google Scholar
117.
Snow CJ, Henry CA: Dynamic formation of microenvironments at the myotendinous junction correlates with muscle fiber morphogenesis in zebrafish. Gene Expr Patterns. 2009, 9: 37-42.
PubMed CAS PubMed Central Google Scholar
118.
Henry CA, McNulty IM, Durst WA, Munchel SE, Amacher SL: Interactions between muscle fibers and segment boundaries in zebrafish. Dev Biol. 2005, 287: 346-360.
PubMed CAS Google Scholar
119.
Daggett DF, Domingo CR, Currie PD, Amacher SL: Control of morphogenetic cell movements in the early zebrafish myotome. Dev Biol. 2007, 309: 169-179.
PubMed CAS PubMed Central Google Scholar
120.
Cortes F, Daggett D, Bryson-Richardson RJ, Neyt C, Maule J, Gautier P, Hollway GE, Keenan D, Currie PD: Cadherin-mediated differential cell adhesion controls slow muscle cell migration in the developing zebrafish myotome. Dev Cell. 2003, 5: 865-876.
PubMed CAS Google Scholar
121.
Barresi MJ, Stickney HL, Devoto SH: The zebrafish slow-muscle-omitted gene product is required for Hedgehog signal transduction and the development of slow muscle identity. Development. 2000, 127: 2189-2199.
PubMed CAS Google Scholar
122.
Du SJ, Devoto SH, Westerfield M, Moon RT: Positive and negative regulation of muscle cell identity by members of the hedgehog and TGF-beta gene families. J Cell Biol. 1997, 139: 145-156.
PubMed CAS PubMed Central Google Scholar
123.
Zebrafish, A Practical Approach. Edited by: Nüsslein-Volhard C, Dahm R. 2002, Oxford, UK: Oxford University Press
124.
Lyche JL, Gutleb AC, Bergman A, Eriksen GS, Murk AJ, Ropstad E, Saunders M, Skaare JU: Reproductive and developmental toxicity of phthalates. J Toxicol Environ Health B Crit Rev. 2009, 12: 225-249.
PubMed CAS Google Scholar
125.
Westerfield M: The Zebrafish Book, A guide for the laboratory use of zebrafish (Danio rerio). 2007, Eugene: University of Oregon Press, 5
Google Scholar
126.
Downes GB, Granato M: Supraspinal input is dispensable to generate glycine-mediated locomotive behaviors in the zebrafish embryo. J Neurobiol. 2006, 66: 437-451.
PubMed CAS Google Scholar
127.
Detrich HW, Kieran MW, Chan FY, Barone LM, Yee K, Rundstadler JA, Pratt S, Ransom D, Zon LI: Intraembryonic hematopoietic cell migration during vertebrate development. Proc Natl Acad Sci USA. 1995, 92: 10713-10717.
PubMed CAS PubMed Central Google Scholar
128.
Weinstein BM, Stemple DL, Driever W, Fishman MC: Gridlock, a localized heritable vascular patterning defect in the zebrafish. Nat Med. 1995, 1: 1143-1147.
PubMed CAS Google Scholar
129.
Weinstein B: Microangiography Method. [http://zfish.nichd.nih.gov/zfatlas/IntroPage/angiography.html]
130.
Barresi MJ, Hutson LD, Chien CB, Karlstrom RO: Hedgehog regulated Slit expression determines commissure and glial cell position in the zebrafish forebrain. Development. 2005, 132: 3643-3656.
PubMed CAS Google Scholar
131.
Jowett T: Tissue In Situ Hybridization: Methods in Animal Development. 1997, New York: John Wiley & Sons, Inc
Google Scholar
132.
Grider MH, Chen Q, Shine HD: Semi-automated quantification of axonal densities in labeled CNS tissue. J Neurosci Methods. 2006, 155: 172-179.
PubMed CAS Google Scholar

Download references

Acknowledgements

We thank British Petroleum for providing us with a sample of Macondo crude oil (MC 252; ID#: 20100617-121) from the Deepwater Horizon oil spill. Special thanks to Nathan Lawson for his consultation on microangiography procedures and providing us with the tg[fli:eGfp] transgenic fish. We appreciate the input and critiques on this work provided by members of the Barresi Lab, David Smith and Thomas Zoeller. We thank Kimberly Johnson for her technical support. The fish husbandry and care provided by the Smith College animal care staff is greatly appreciated. A truly special thanks to all the students of the 2010 BIO303, Research in Developmental Biology course, who began the preliminary analysis of Macondo crude oil on zebrafish development. This work was funded by Smith College, NSF 0615594, NSF 1054168, NIH HD060023 to MJB, ACS PF-08-159-01-DDC to RLB, Henry Dreyfus Teacher Scholar Award to SH, and K01-NS057409 to GBD.

Author information

Affiliations

Biological Sciences, Smith College, Northampton, MA, 01063, USA
T Yvanka de Soysa, Allison Ulrich, Danielle Pite, Shannon L Compton, Deborah Ok, Rebecca L Bernardos, Shizuka Hsieh, Rachael Stein, M Caterina Lagdameo, Katherine Halvorsen, Lydia-Rose Kesich & Michael JF Barresi
Molecular and Cellular Biology, University of Massachusetts, Amherst, MA, USA
Timo Friedrich & Gerald B Downes

Authors

T Yvanka de Soysa
View author publications
You can also search for this author in PubMed Google Scholar
Allison Ulrich
View author publications
You can also search for this author in PubMed Google Scholar
Timo Friedrich
View author publications
You can also search for this author in PubMed Google Scholar
Danielle Pite
View author publications
You can also search for this author in PubMed Google Scholar
Shannon L Compton
View author publications
You can also search for this author in PubMed Google Scholar
Deborah Ok
View author publications
You can also search for this author in PubMed Google Scholar
Rebecca L Bernardos
View author publications
You can also search for this author in PubMed Google Scholar
Gerald B Downes
View author publications
You can also search for this author in PubMed Google Scholar
Shizuka Hsieh
View author publications
You can also search for this author in PubMed Google Scholar
Rachael Stein
View author publications
You can also search for this author in PubMed Google Scholar
M Caterina Lagdameo
View author publications
You can also search for this author in PubMed Google Scholar
Katherine Halvorsen
View author publications
You can also search for this author in PubMed Google Scholar
Lydia-Rose Kesich
View author publications
You can also search for this author in PubMed Google Scholar
Michael JF Barresi
View author publications
You can also search for this author in PubMed Google Scholar

Corresponding author

Correspondence to Michael JF Barresi.

Additional information

Competing interests

The authors declare that they have no competing interests.

Authors' contributions

TS participated in experiment design and played a role in carrying out many of the experiments in this study with particular efforts on all cardiovascular, craniofacial, and neural crest analysis. AU contributed significantly to initial experimental design of this study as well as carried out most of the initial replicates. TF carried out the behavioral analysis of touch responsiveness and the kinematics of swimming. DP carried out a majority of the analysis of WAF chemical composition. SC carried out a majority of the refreshing WAF treatments and experiments as well as performed many of the statistical analyses. DO assisted in a majority of embryo treatments as well as supported immunocytochemistry experiments. RB provided assistance on all immunocytochemistry, embryo treatments and imaging on the AxioImager. GD designed, monitored and participated in the behavioral analysis. SH designed, monitored and participated in the chemical analysis of WAF components. RS assisted in data collection for the analysis of cell death. MCL performed the initial experiments on slow muscle development. KH designed and supported the statistical analysis of collected data. LK supported many of the final experiments of this work contributing directly to the acquisition of fli:GFP and dlx2 data. MB conceived of the study, substantially contributed to the design, coordination, and implementation of many of the experiments, with particular contributions to microangiography procedures, and cartilage and neural crest imaging. MB participated in all data and statistical analysis and drafted the manuscript. All authors read, contributed feedback to, and approved the final manuscript.

T Yvanka de Soysa, Allison Ulrich contributed equally to this work.

Electronic supplementary material

Additional file 1: Initial assessment of water accumulated fractions. This file provides greater explanation of the methods and results associated with our WAF mixing procedure, as well as initial assessments of the effects of different WAF concentrations on the development of zebrafish gross morphology. (PDF 37 KB)

Expanded WAF chemical analysis

Additional file 2: . This file provides a detailed list of all the compounds and concentrations discovered following gas chromatography mass spectrometry analysis of our WAF. Supplemental Table S1: GCMS parameters for Agilent 7890A GC/5975C MSD. Supplemental Table S2: Aqueous solubilities and Henry's constants for selected hydrocarbons. Supplemental Table S3: Most prominent GCMS peaks in WAF. Supplemental Figure S1: Relative detection efficiencies of the SPME/GCMS method for selected aromatics and alkanes. Supplemental Figure S2: Total ion chromatogram. Supplemental Figure S3: Total ion chromatograms for the aqueous portion of a WAF sample and for a sample that includes some of the oily layer. (PDF 2 MB)

Authors’ original submitted files for images

Below are the links to the authors’ original submitted files for images.

Authors’ original file for figure 1

Authors’ original file for figure 2

Authors’ original file for figure 3

Authors’ original file for figure 4

Authors’ original file for figure 5

Authors’ original file for figure 6

Authors’ original file for figure 7

Authors’ original file for figure 8

Authors’ original file for figure 9

Rights and permissions

Reprints and Permissions

About this article

Cite this article

de Soysa, T.Y., Ulrich, A., Friedrich, T. et al. Macondo crude oil from the Deepwater Horizon oil spill disrupts specific developmental processes during zebrafish embryogenesis. BMC Biol 10, 40 (2012). https://doi.org/10.1186/1741-7007-10-40

Download citation

Received: 30 March 2012
Accepted: 04 May 2012
Published: 04 May 2012
DOI: https://doi.org/10.1186/1741-7007-10-40

Keywords

Deepwater Horizon
crude oil
zebrafish
embryonic development
cardiovascular
cartilage
neural crest
peripheral nervous system
somitogenesis
muscle

Macondo crude oil from the Deepwater Horizon oil spill disrupts specific developmental processes during zebrafish embryogenesis

Abstract

Background

Results

Conclusions

Introduction

Results

Gross morphological deformations

Chemical analysis of water accumulated fraction

Cell proliferation and cell death

Circulation and vasculogenesis

Craniofacial development

Locomotor behavior

Neuronal development in the central and peripheral nervous system

Somitogenesis and muscle fiber type development

Discussion

Defects in size and shape through induction of apoptosis

Selective impairment of neural crest cells is at the 'heart' of the problem

Defects in patterning the peripheral nervous system impacts locomotor escape behaviors

Phenotypic changes over time

Conclusions

Methods

Sampled Macondo crude oil

Water accommodated fraction (WAF)

WAF chemical analysis

Embryo collection and treatment

Behavioral analysis

Blood, circulation and vascular analysis

Immunohistochemistry and imaging

Quantitation and statistics

Authors' information

Abbreviations

References

Acknowledgements

Author information

Affiliations

Corresponding author

Additional information

Competing interests

Authors' contributions

Electronic supplementary material

Authors’ original submitted files for images

Rights and permissions

About this article

Cite this article

Keywords

BMC Biology

Contact us