The nematode Caenorhabditis elegans is being assessed as an alternative model organism as part of an interagency effort to develop better means to test potentially toxic substances. As part of this effort, assays that use the COPAS Biosort flow sorting technology to record optical measurements (time of flight (TOF) and extinction (EXT)) of individual nematodes under various chemical exposure conditions are being developed. A mathematical model has been created that uses Biosort data to quantitatively and qualitatively describe C. elegans growth, and link changes in growth rates to biological events. Chlorpyrifos, an organophosphate pesticide known to cause developmental delays and malformations in mammals, was used as a model toxicant to test the applicability of the growth model for in vivo toxicological testing.
L1 larval nematodes were exposed to a range of sub-lethal chlorpyrifos concentrations (0–75 µM) and measured every 12 h. In the absence of toxicant, C. elegans matured from L1s to gravid adults by 60 h. A mathematical model was used to estimate nematode size distributions at various times. Mathematical modeling of the distributions allowed the number of measured nematodes and log(EXT) and log(TOF) growth rates to be estimated. The model revealed three distinct growth phases. The points at which estimated growth rates changed (change points) were constant across the ten chlorpyrifos concentrations. Concentration response curves with respect to several model-estimated quantities (numbers of measured nematodes, mean log(TOF) and log(EXT), growth rates, and time to reach change points) showed a significant decrease in C. elegans growth with increasing chlorpyrifos concentration.
Effects of chlorpyrifos on C. elegans growth and development were mathematically modeled. Statistical tests confirmed a significant concentration effect on several model endpoints. This confirmed that chlorpyrifos affects C. elegans development in a concentration dependent manner. The most noticeable effect on growth occurred during early larval stages: L2 and L3. This study supports the utility of the C. elegans growth assay and mathematical modeling in determining the effects of potentially toxic substances in an alternative model organism using high-throughput technologies.
Citation: Boyd WA, Smith MV, Kissling GE, Rice JR, Snyder DW, et al. (2009) Application of a Mathematical Model to Describe the Effects of Chlorpyrifos on Caenorhabditis elegans Development. PLoS ONE 4(9): e7024. doi:10.1371/journal.pone.0007024
Editor: Anne C. Hart, Massachusetts General Hospital/Harvard Medical School, United States of America
Received: May 13, 2009; Accepted: August 7, 2009; Published: September 15, 2009
This is an open-access article distributed under the terms of the Creative Commons Public Domain declaration which stipulates that, once placed in the public domain, this work may be freely reproduced, distributed, transmitted, modified, built upon, or otherwise used by anyone for any lawful purpose.
Funding: This work was supported (in part) by the Intramural Research Program of the NIH and NIEHS (Z01ES102046), and the National Toxicology Program. The work of Dr. Smith was supported by the NIEHS contract #GS-00F-0003L. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The work of Dr. Smith was supported by the National Institute of Environmental Health Sciences contract #GS-00F-0003L to SRA International.
The U. S. Environmental Protection Agency estimates that there are at least 10,000 chemicals that require testing to evaluate their potential threat to human and environmental health . Due to the need to screen such a large number of chemicals, three government agencies; the Environmental Protection Agency, National Toxicology Program and the NIH Chemical Genomics Center; signed an agreement to transform predictive toxicity testing from mainly in vivo mammalian studies to tests using alternative species and in vitro high-throughput screens . The goals are to (a) develop reliable assays using alternative organisms or cell-based assays, (b) collect high-quality data using those assays, and then (c) assess whether those data can predict human toxicity.
One alternative animal model that has proven useful in toxicological research is the nematode Caenorhabditis elegans . A strength of C. elegans as a model organism is the high degree of evolutionary conservation in its biological processes . In addition, many of the stress response pathways, including those induced by exposure to environmental chemicals, are well-conserved .
C. elegans are self-fertilizing hermaphrodites that produce hundreds of genetically-identical offspring over several days of adulthood. C. elegans hatch into their first larval stage (L1) and continue to develop to adults through three additional distinct larval stages, L2-L4 . Between each larval stage, nematodes grow in bursts by molting old cuticles . C. elegans cultures can be synchronized by hatching embryos in the absence of food, causing L1 development to arrest . The L1 larvae resume normal growth when food is introduced and mature as a synchronous population to gravid adults in approximately 60 h at 20°C .
Observations of up to 6,000 C. elegans/per minute can be made using the COPAS Biosort flow sorting system, which is designed to sort, dispense and measure various parameters of individual nematodes . The Biosort measures and records up to four attributes for each individual: time of flight (TOF), which relates to nematode length; extinction (EXT), which corresponds to the optical density; and two fluorescence measurements. TOF and EXT measurements are related to the age and size of the nematode; both increase as C. elegans develop.
Assays and analytical methods have been developed that utilize the Biosort output to answer questions about C. elegans biology and the effects of toxicants –. A growth assay in which synchronized L1s are loaded into 96 well plates, incubated in the presence of toxicants, and their size distribution measured at later times has been developed. To accurately measure C. elegans growth in the presence and absence of toxicants, a mathematical model that describes changes in C. elegans size distributions as increases in EXT and TOF during nematode maturation was created . A mathematical model was necessary to estimate C. elegans growth rates and size distributions due to the nature of the data generated by the Biosort, which were not directly amenable to rigorous statistical analysis. The Biosort provides EXT and TOF measurements of each nematode at loading (t = 0 h) and of the same set of nematodes at the end of the growth period. Initial measurements on an individual nematode, however, can not be matched to its final measurements at the end of the study. This type of data contrasts with growth measurements using cell culture, in which changes in the population are represented by single values (e.g., optical density, total cell number), or larger animal data in which changes in the growth (e.g., weight, height) can be assigned to an individual subject. Therefore, the C. elegans growth model mathematically describes the distributions of measurements on a set of nematodes, allowing means and average growth rates to be calculated.
One feature of the Biosort data that also needed to be addressed by the model was the presence of extraneous material such as shed cuticles or clumps of bacteria, which accumulate as C. elegans develop over time. Measurements on this extraneous material can not be automatically distinguished from those on the nematodes, and thus could affect statistical analyses. By mathematically modeling the distribution of measurements on the extraneous material, the model accounts for the extraneous matter and allows for a more accurate analysis of nematode growth.
In the present report, the growth model has been applied to test its effectiveness in detecting statistically significant differences in C. elegans development in the presence of a toxicant. The output from the analysis includes the effects of toxicant concentration and exposure time on three phases of C. elegans growth. To test and refine the growth assay, C. elegans were exposed to the environmentally-relevant, developmental neurotoxicant: chlorpyrifos. Chlorpyrifos is one of the most commonly applied organophosphate pesticides . Organophosphate pesticides constitute almost half of all of the insecticides used worldwide . In addition to its activity as a cholinesterase inhibitor, data suggest that chlorpyrifos may cause decreased DNA synthesis and developmental alterations , . Growth retardation has also been observed in children exposed to chlorpyrifos in utero . Due to adverse human and environmental health effects, chlorpyrifos has been banned for use in homes, schools, and hospitals .
EXT and TOF measurements on nematodes exposed to various chlorpyrifos concentrations were sampled over a 72 h period. Estimated numbers of nematodes and average growth rates based on EXT and TOF measurements were then calculated using the model. These estimates showed significant decreases in both numbers of nematodes and their growth rates as a function of chlorpyrifos concentration. In addition, L2 and L3 larvae were the most sensitive to chlorpyrifos exposure.
C. elegans growth and model
Data from the two chlorpyrifos exposure studies were combined and analyzed using the C. elegans Markov growth model . Each study consisted of thirty-six cohorts each containing 300 L1 nematodes. Six cohorts were exposed to one of five chlorpyrifos concentrations or an untreated control. Following 12, 24, 36, 48, 60, and 72 h incubations at 20°C, one cohort at each concentration was measured in the Biosort to determine its distribution of EXT and TOF.
Distributions of log(EXT) at each of the six time points for the control cohorts are presented in Figure 1. These distributions shifted to the right with increasing incubation time; L1s loaded at t = 0 h had a peak frequency at log(EXT) value near 3.1, while nematodes observed following 60 h and 72 h incubations had peak frequency at log(EXT) values near 6.3. Optical density, as measured by EXT, tends to increase as nematodes mature . Microscopic observations showed that L1 nematodes matured to L2s by 12 h, L3s by 24 h, L4s by 48 h, and adults by 60 h. After 60 h, adults showed a small increase in optical density but mainly produced offspring. The large numbers of measurements with log(EXT) values between 2 to 3.4 observed at 60 h and 72 h included unhatched embryos laid by the adults and the next generation of L1 larvae.
Figure 1. C. elegans growth from L1 to adult.
Nematode frequency distributions of log(EXT) values for control nematode cohorts sampled at loading 0 h (brown) and following 12 (green), 24 (light blue), 36 (purple), 48 (black), 60 (dark blue), and 72 (red) h incubations. Large modes to the left of the loaded nematodes (log(EXT) ≈2–3) indicate the second generation of embryos corresponding to 60 and 72 h cohorts. Vertical lines at log(EXT) = 3.83 and 6.04 divide the growth response into three sections: initial growth from starved L1s, larval growth from L2 to L4, and adult growth, respectively.doi:10.1371/journal.pone.0007024.g001
Under normal conditions C. elegans growth was thought to be approximately exponential ; therefore, growth rates with respect to either log(EXT) or log(TOF) should be fairly constant. We previously reported, however, that the best fitting model for either log(EXT) or log(TOF) contained three separate growth rates, separated by two change points . The three sections in control nematodes are indicated in Figure 1 by vertical lines: log(EXT) = 3.83 and 6.04. Microscopic observations indicated that these sections contained embryos and L1s (2–3.83); L2, L3 and L4 larvae (3.83–6.04); and adults (6.04–7.00).
Effect of chlorpyrifos on the nematode frequency distribution
Chlorpyrifos was used to study the applicability of the mathematical model in determining the effects of chemicals on C. elegans growth. Two experiments using different ranges of sub-lethal chlorpyrifos concentrations, 0–50 and 0–75 µM, were performed and the data combined to determine the effects on growth. The lowest concentration (0.5 µM) did not affect growth compared to untreated controls and the highest concentration (75 µM) completely inhibited growth, as determined by microscopic observation. Frequency distributions for log(EXT) and log(TOF) at each time point for the first experiment are presented in Figure 2. The frequency distributions for the second experiment are in Supporting Information File S1.
Figure 2. Effects of chlorpyrifos on C. elegans growth.
Frequency distributions of log(EXT) (left column) and log(TOF) (right column) on nematodes exposed to 0, 0.5, 5, 15, 30, and 50 µM chlorpyrifos following 12 (green), 24 (light blue), 36 (purple), 48 (black), 60 (dark blue), and 72 (red) h incubations. Vertical lines indicate change points at log(EXT) = 3.83 and 6.04 and log(TOF) = 4.04 and 5.28.doi:10.1371/journal.pone.0007024.g002
At the lowest concentration of chlorpyrifos tested (0.5 µM), the frequency distribution at each time point was nearly identical to that observed in control nematodes, indicating that chlorpyrifos did not affect C. elegans development. Furthermore, the close similarity at 60 and 72 h suggested that control nematodes and those exposed to 0.5 µM chlorpyrifos had fully developed to reproductive adults by 60 h (Fig. 2 and Supporting Information File S1). Above 0.5 µM, concentration-dependent decreases in growth were observed. At the highest concentration tested, 75 µM, the distributions did not shift to the right with time (Supporting Information File S1), suggesting that 75 µM chlorpyrifos completely inhibited nematode growth.
Nematodes exposed to chlorpyrifos concentrations greater than 45 µM did not develop beyond the second change point within 72 h (Fig. 2, Supporting Information File S1). Microscopic observations made at 72 h verified that, at concentrations below 30 µM, nematodes developed to the adult stage, but were smaller in size. C. elegans exposed to concentrations greater than 30 µM did not reach adulthood and at 75 µM did not develop beyond the L2 stage (Supporting Information File S1).
The observed and model-estimated frequency distributions of log(EXT) and log(TOF) values for cohorts exposed to 30 µM are presented in Figure 3. Plots for other concentrations are presented in Supporting Information File S2 for log(EXT) and Supporting Information File S3 for log(TOF) measurements. Extraneous matter; such as detritus, clumps of bacteria, and embryos; can not be distinguished from nematodes directly from log(EXT) and log(TOF) measurements. For this reason, measurements were modeled using a mixture of a Markov model for the nematodes and a lognormal distribution for the extraneous matter (see Methods). This mixture model accurately described the distributions of log(TOF) and log(EXT) at each time point (i.e., compare red lines versus blue lines in Figure 3). At all exposure levels and time points, model-predicted frequency distributions agreed well with the observed frequency distributions. (It should be noted that the word prediction is used in this paper to refer to estimates made from the model after optimization, much as any calculated output from any model may be referred as a prediction. It does not refer to predictions made for use with other data or in different circumstances. The value of the model for the analysis in this paper lies in the estimation of growth rates of nematodes over time under specific conditions, including exposures to possible toxicants.)
Figure 3. Observations and predictions across aspiration times using 30 µM chlorpyrifos.
Observed (red) and model-estimated (blue) frequency distributions of log(EXT) (left column) and log(TOF) (right column). L1 nematodes loaded at the start of the experiment are also presented (green). Vertical lines indicate change points where growth rates changed at log(EXT) = 3.83 and 6.04 and log(TOF) = 4.04 and 5.28. Change points were constant over time and concentration, but differed between log(EXT) and log(TOF). Data for other chlorpyrifos concentrations are shown in Supporting Information Files S2 (log(EXT)) and S3 (log(TOF)).doi:10.1371/journal.pone.0007024.g003
Effect of chlorpyrifos on C. elegans growth
Although the chlorpyrifos concentrations were chosen to be sub-lethal, the model-estimated numbers of nematodes significantly decreased with increasing concentration (Page test; p<0.001). Estimated numbers of nematodes, as well as all other parameter estimates, are presented in Supporting Information File S4. The estimated mean log(EXT) and log(TOF) as functions of chlorpyrifos concentration and observation times are presented in Figure 4. These means diminished significantly as a function of chlorpyrifos concentration at each time point (by linear regression, p<0.01 for log(EXT); p<0.05 for log(TOF)) (Table 1). The strength of the concentration effects, as indicated by the magnitude of the slopes, also increased with exposure time. Taken together, these observations indicate that chlorpyrifos inhibits C. elegans growth in a concentration- and exposure time-dependent fashion.
Figure 4. Effects of chlorpyrifos on mean C. elegans growth.
Estimated means of log(EXT) (left panel) and log(TOF) (right panel) as functions of chlorpyrifos concentration; 0, 0.5, 0.75, 5.0, 7.5, 15, 22.5, 30, 45 and 50 µM; at six sampling times; 12 (green), 24 (light blue), 36 (purple), 48 (black), 60 (dark blue), and 72 (red) h. Statistical significance of concentration effect was tested by fitting straight lines through estimated means and testing slopes. A regression line for the 72 h log(TOF) data is not presented because there was no significant growth between 60 h and 72 h.doi:10.1371/journal.pone.0007024.g004
Table 1. Slopes of mean log(EXT) and log(TOF) as a function of concentration by sampling time.doi:10.1371/journal.pone.0007024.t001
For nematodes exposed to 0 and 0.5 µM chlorpyrifos, growth was completed by 60 h, so neither the TOF nor EXT measurement changed between 60 and 72 h (Fig. 2). Likewise, nematodes exposed to 75 µM chlorpyrifos grew very little over time, based on the extensive overlap in the distributions of log(TOF) among the time points (Supporting Information File S1). Previously, it was demonstrated that TOF measurements are generally more variable than EXT, and thus have a greater tendency to overlap . In these cases where there is little to no change in TOF or EXT, growth rates can not be estimated by the mathematical model.
The growth model predicts three separate constant growth rates with respect to log(EXT) and log(TOF) measurements. The two points at which the growth rate changes, ‘change points’, are marked by vertical lines in Figures 1, 2, and 3; and divide the log(EXT) and log(TOF) ranges into 3 sections. Varying the change points for nematodes exposed to different chlorpyrifos concentrations did not improve the model fit; therefore change points were held constant for all concentrations at 3.83 and 6.04 for log(EXT) and at 4.04 and 5.28 for log(TOF).
To analyze the effects of chlorpyrifos on the estimated growth rates, a negative exponential function, , was fit to the growth rates in each of the three sections as functions of concentration (Fig. 5; equations for each section are presented in Supporting Information File S5). The strength of the chlorpyrifos effect on the growth rate is indicated by B. The final models for the three sections were chosen using the Akaike information criterion . For every section, B was significantly greater than zero, indicating a significant inhibitory effect of chlorpyrifos on growth. In addition, the effect increased with increasing chlorpyrifos concentration for each of the three sections, further indicating concentration dependent growth inhibition (Fig. 5; Table 2). The functions eventually reached the same minimum growth rate for all three sections (Fig. 5), which may represent the minimum growth rate that the model could detect.
Figure 5. Growth rates of C. elegans after chlorpyrifos exposure.
Estimated growth rates of log(EXT) per h (left panel) and log(TOF) per h (right panel) as functions of chlorpyrifos concentration. Growth rates are shown for three sections: initial growth rates before the first change point (blue), growth rates between change points (red), and growth rates after the second change point (green). Solid lines correspond to negative exponential functions with a common lower asymptote fit to the estimated growth rates. Nematodes exposed to chlorpyrifos concentrations greater than 30 µM did not grow to the third section.doi:10.1371/journal.pone.0007024.g005
Table 2. Growth rates at each chlorpyrifos concentration.doi:10.1371/journal.pone.0007024.t002
The expected length of time needed for a nematode to reach each change point was computed from the estimated growth rates (Fig. 6), and then straight lines were fit as functions of concentration. The final models for both change points were chosen using the Akaike information criterion . The expected time for L1s to develop and reach the first change point was similar in the controls for both log(EXT) and log(TOF), approximately 10 h, and increased significantly with chlorpyrifos concentration. Expected length of time to reach the first change point, based on optical density (log(EXT)), was somewhat more affected by increasing chlorpyrifos concentration than that based on nematode length (log(TOF)), as indicated by the steeper slope (Fig. 6). These results are consistent with the visual observations that chlorpyrifos-exposed nematodes appeared to be starved and thinner than controls, but not shorter in length (Table 3). The expected length of time for L1s to develop to the second change point also showed a concentration-dependent increase for both log(EXT) and log(TOF). These observations further demonstrate the inhibitory effects of chlorpyrifos on growth. In contrast to the time to reach the first change point, for the second change point there was a consistent 17 h difference between log(TOF) and log(EXT), regardless of chlorpyrifos concentration.
Figure 6. Effect of chlorpyrifos on the estimated times to change points.
Regression lines correspond to the time required for the C. elegans cohort to develop to the first (dotted line) or the second (solid line) change point for log(EXT) (red) and log(TOF) (blue) values. For the first change point, log(EXT) and log(TOF) times at lower chlorpyrifos concentrations (0.5 and 0.75 µM) are indistinguishable from control nematodes while, at higher concentrations, log(EXT) was more affected than log(TOF). In contrast, the difference in time to reach the second change point between log(TOF) and log(EXT) is 17 h, regardless of chlorpyrifos concentration.doi:10.1371/journal.pone.0007024.g006
Table 3. Visual observations made near change points.doi:10.1371/journal.pone.0007024.t003
Effect of chlorpyrifos on change points
Although numbers of nematodes and their growth rates were affected by chlorpyrifos concentration, the positions of the estimated change points for both log(EXT) and log(TOF) were unaffected. That is, the rates for the three phases of C. elegans growth were affected by chlorpyrifos, but the log(EXT) and log(TOF) values during C. elegans development at which growth rates changed remained the same. Microscopic observations of non-exposed nematodes at the change points indicated that the first change point coincided with the L1 to L2 molt, while the second change point occurred near the L3 to L4 molt for log(TOF), and at the onset of egg production in young adults for log(EXT) values (Table 3).
Microscopic observations of selected chlorpyrifos-exposed nematodes were made at times corresponding to the change points: observations made at the times corresponding to first change point for both EXT and TOF (Table 3A); observations made near the expected time for the second log(TOF) change point (Table 3B); and observations made near the expected time for the second change point for the log(EXT) measurements (Table 3C). While chlorpyrifos increased the time to reach each change point, it did not substantially alter the composition of the cohort (Table 3B and 3C). Thus, the growth rates during these phases of C. elegans growth were affected by chlorpyrifos, but the biological events that occurred at the three change points during development were not affected by chlorpyrifos. Combining the information on the effects of chlorpyrifos on the time required to reach the change points (Fig. 6) with the visual observations of C. elegans at the change points (Table 3) led to the conclusion that the greatest developmental effect of chlorpyrifos was to increase the duration of the L2 and L3 larval stages and to delay the L3/L4 molt. For control nematodes, the length of time between the L1/L2 molt (first log(TOF) change point) and the L3/L4 molt (second log(TOF) change point) was approximately 27 h for control nematodes and was 52 h for nematodes exposed to 50 µM chlorpyrifos. In contrast, the length of time between the L3/L4 molt (second log(TOF) change point) and the onset of egg production (second log(EXT) change point) remained constant at about 17 h, regardless of level of exposure. Thus, once nematodes reached the L3/L4 molt, further development was not significantly affected by chlorpyrifos.
Chemical effects on C. elegans can be quantified using a variety of endpoints such as feeding behavior, locomotion, and egg-laying , , . In this report, the applicability of a quantitative medium-throughput growth assay, analyzed using a mathematical model to determine the effects of chemicals on C. elegans was presented. These results confirmed the validity of this model, which provided information on chemical-induced changes in numbers of nematodes and growth rates. In addition, the concentration dependence of these effects was clearly demonstrated and quantified.
Many C. elegans studies have reported the measurement of abnormal growth phenotypes, mainly by measuring the delay to a predetermined developmental stage such as molting. The timing of molts, however, and the regulation of developmental rates within each larval stage have been poorly characterized . Several studies have measured nematode length or volume using microscope reticles or image capture software , . Although these methods are quantitative, they are tedious and can only be used to characterize small numbers of nematodes, and thus have limited statistical power. The COPAS Biosort is able to rapidly record measurements of length and optical density on large numbers of nematodes. Until now however, the data provided by the Biosort have not been quantitatively analyzed in a way that provides insight into the biology associated with chemical treatments. In applying the Markov model for growth  to nematodes exposed to the developmental toxicant chlorpyrifos, concentration effects can be accurately described. Once properly described, statistical tests for significance in changes in numbers of nematodes, mean log(EXT) or log(TOF) values, or estimated growth rates can be determined.
The optimal form of the model describes growth as piecewise linear over time, based on both log(EXT) and log(TOF). The times at which the growth rates change, referred to as change points, are associated with L1 to L2 molts for both log(EXT) and log(TOF), L3 to L4 molts for log(TOF), and the onset of egg production in young adults for log(EXT) . Visual examination of nematodes near the estimated times for growth rate change in the current study verified that these characterizations are reproducible between different studies. In addition, while exposure to chlorpyrifos prolongs the times to reach the change points, it does not significantly change the composition of the cohort of nematodes at the change points. Thus, this model provides a link between rapidly produced Biosort data and biological events such as specific molts or onset of egg production.
The effect of chlorpyrifos exposure on the time required to reach a change point was not proportional to the toxicant concentration at all stages of development. The length of time between the L1/L2 molt and the L3/L4 molt increased from approximately 27 h for untreated nematodes to 52 h for nematodes exposed to 50 µM chlorpyrifos. The length of time between the L3/L4 molt and onset of egg production, however, was concentration independent and remained constant at 17 h. The difference between the second log(TOF) change point (L3/L4 molt) and the second log(EXT) change point (onset of egg production in adulthood) were consistent with published observations, which showed that at 20°C the L4/adult molt occurred approximately 13 h after the L3/L4 molt and the first embryos were laid 21.5 h after the L3/L4 molt . Thus, in addition to characterizing an overall inhibition of nematode growth by chlorpyrifos, L2 and L3 larvae were identified as more susceptible to chlorpyrifos toxicity than later larvae or adults.
Exposure to chlorpyrifos in mammalian systems is associated with the inhibition of neuronal development . Interestingly, the development of much of the ventral nervous system in C. elegans occurs during the early larval stages . An additional 80 neurons (~30% of the C. elegans nervous system) are born during L1 and L2 stages . The growth assay may have also identified a relation between the growth inhibitory effects associated with chlorpyrifos exposure and neural development. This suggests that this assay may identify subtle effects of toxicant exposure during specific periods in C. elegans development. Additional studies will be required to confirm a neurodevelopmental affect of chlorpyrifos exposure.
C. elegans growth and development are known to be substantially affected by exposure to aldicarb, another cholinesterase inhibitor . Prolonged exposure or exposure to high doses of aldicarb may also decrease feeding, leading to an indirect effect on nematode growth . The effect of chlorpyrifos on C. elegans feeding, as measured by the accumulation of fluorescent-labeled microspheres, has been previously reported. A 50% inhibition of feeding at 1.3 µM chlorpyrifos (95% C.I. = 0–9.2) was observed . In this study, nematodes were observed with a ‘starved’ appearance following exposure to chlorpyrifos concentrations greater than 7.5 µM (Table 3). This suggests that starvation may be a contributing factor to chlorpyrifos-induced growth inhibition.
A hallmark of high-throughput screening is automation of data collection, which rapidly produces large quantities of data. Linking quantitative data to biological events allows for the interpretation of trends and differences. In this report, high-throughput data from the Biosort was combined with a mathematical model of C. elegans growth. Modeling of C. elegans development allowed for the estimation of several growth parameters including number of nematodes, mean population distribution, and growth rates. Statistical analyses of these parameters showed concentration-dependent decreases in both numbers of nematodes and growth rates as a result of chlorpyrifos exposure. Although chlorpyrifos affected the time to reach the change points, the biological events that occurred at those points were not affected. In addition, the model indicated that the greatest chlorpyrifos effects occurred during larval stages L2 and L3.
The precise mechanism by which chlorpyrifos affected C. elegans growth could not be determined using these assays. Regardless of the mechanism of the developmental delay, if the effects of chemicals on C. elegans growth are predictive of mammalian toxicity, then C. elegans assays may prove to be valuable additions to in vivo high-throughput toxicity screens of the large number of chemicals that need to be assayed before mammalian testing.
The Bristol N2 C. elegans strain was obtained from the Caenorhabditis Genetic Center (Minneapolis, MN), and maintained at 20°C on K-agar plates seeded with E. coli OP50 as a food source , . Synchronized L1 cultures were prepared as previously described , except that embryos were hatched overnight at 20°C in vented T25 flasks containing complete K-medium (51 mM sodium chloride, 32 mM potassium chloride, 3 mM calcium chloride, 3 mM magnesium sulfate, 13 µM cholesterol).
L1 nematodes were transferred to the sample cup of the COPAS Biosort – (Union Biometrica Inc., Somerville, MA, USA) and diluted to approximately 1 nematode/µL. Twenty-five L1s were then added to each well of a 96-well plate, containing a total volume of 50 µL complete K-medium, streptomycin-killed (1 mg/kg) E. coli, diluted to an A550 = 0.5–0.55, and chlorpyrifos (Chem Service, Westchester, PA; CAS#2921-88-2).
Chlorpyrifos stocks were prepared in DMSO. The final concentration of DMSO used in these studies was 1% (v/v), a concentration that does not affect nematode growth (data not shown). Two experiments were performed using six different chlorpyrifos concentrations with cohorts measured every 12 h for 72 h. A cohort consisted of 300 nematodes per treatment condition (25 nematodes per well×12 wells). Two different concentration series were tested in the two experiments: 0, 0.5, 5.0, 15, 30 and 50 µM, and 0, 0.75, 7.5, 22.5, 45 and 75 µM. C. elegans cohorts were incubated without shaking for 12, 24, 36, 48, 60 and 72 h at 20°C and then TOF and EXT measurements of individual nematode were acquired with the COPAS Biosort ReFLx. All COPAS Biosort measurements were performed with EXT signal gain of 80, EXT integral gain of 100, EXT signal threshold of 80, and TOF minimum of 10.
Study design and model description
Both log(EXT) and log(TOF) measurements were analyzed using the Markov model applied to C. elegans growth previously described . Briefly, a frequency distribution of measurements is constructed using a grid of bins encompassing the observed range of log(EXT) or log(TOF) values. Growth of nematodes is modeled by assuming that over each 12 h interval, nematodes grow sufficiently that their measurements shift to the right 10, 11, or 12 bins. The probabilities of growing 10, 11, or 12 bins are used to define a transfer probability or growth matrix, G. Using the distribution of measurements taken at loading, f0, the distribution of the same cohort at aspiration 12×k h later, fk, is predicted by the formula:(1)
In addition to nematodes, extraneous material accumulated in the wells is also measured by the Biosort. These extraneous measurements, which may be discarded cuticles, clumped bacteria, or chemical precipitates, are not individually separable from nematode measurements. The extraneous measurements are represented in the model by a lognormal distribution. The total set of measurements acquired at sampling time k (nematodes and extraneous) is modeled as a weighted average of the lognormal distribution and the distribution, fk, predicted by the Markov model. The weights estimated for the lognormal and modeled distributions reflect the fractions of the total measurements ascribed to extraneous observations and nematodes, respectively.
The model allows 12 h growth across a constrained number of bins (i.e., 10, 11, or 12); growth rates are reflected by the size of the bins. Using least squares, the difference between observed and estimated frequency distributions of nematodes is minimized by adjusting bin sizes, where larger bins correspond to faster growth rates. In this study, changes in log(EXT) and log(TOF) measurements are best approximated by piecewise constant growth rates, with two change points dividing the range of measurements into three sections. In addition to estimating growth rates, the expected time for a nematode to reach a change point is calculated by averaging the time needed to shift the required number of bins to the right over the loading distribution.
A distribution-free test for trend (Page test), blocking on observation time, was used to test whether concentration-related trends in numbers of nematodes were significant . Application of the Page test requires a balanced design, so the estimated numbers of nematodes for the 72 h aspirations (available only for the higher concentrations) could not be used. The linear associations between exposure concentration and mean log(EXT), mean log(TOF) or time to change points were tested for significance using standard regression tests (F-tests; ). Negative exponential curves were fit to the estimated growth rates, and straight lines were fit to the estimated times to change points. Optimal models for growth rates and times to change points were chosen using the Akaike information criterion .
Nematode strains used in this work were provided by the Caenorhabditis Genetics Center, which is funded by the NIH National Center for Research Resources. The authors thank Matthew McElwee for his thoughtful comments.
Frequency distributions of (a) log(EXT) and (b) log(TOF) on nematodes exposed to 0, 0.75, 7.5, 22.5, 45, and 75 µM chlorpyrifos at 12, 24, 36, 48, 60, and 72 h. Vertical lines divide the growth response into 3 sections: initial growth from starved L1s, larval growth from L2-L4, and adult growth.
(0.04 MB PDF)
Observed (red) and model-predicted (blue) distributions of log(EXT). The distribution of the loaded nematodes is shown in green. Extraneous noise was modeled as a lognormal
(0.08 MB PDF)
Observed (red) and model-predicted (blue) distributions of log(TOF). The distribution of the loaded nematodes is shown in green. Extraneous noise was modeled as a lognormal distribution (black). Black vertical lines indicate change points, where growth rates changed.
(0.08 MB PDF)
(0.07 MB PDF)
Negative exponential functions fit to growth rates.
(0.01 MB PDF)
Conceived and designed the experiments: WAB CJP JHF. Performed the experiments: JRR DWS. Analyzed the data: WAB MVS GEK CJP. Wrote the paper: WAB MVS CJP JHF.
- 1. Dix DJ, Houck KA, Martin MT, Richard AM, Setzer RW, et al. (2007) The ToxCast program for prioritizing toxicity testing of environmental chemicals. Toxicol Sci 95: 5–12.
- 2. Collins FS, Gray GM, Bucher JR (2008) Toxicology. Transforming environmental health protection. Science 319: 906–907.
- 3. Leung MC, Williams PL, Benedetto A, Au C, Helmcke KJ, et al. (2008) Caenorhabditis elegans: an emerging model in biomedical and environmental toxicology. Toxicol Sci 106: 5–28.
- 4. The C. elegans Sequencing Consortium (1998) Genome sequence of the nematode C. elegans: a platform for investigating biology. Science 282: 2012–2028.
- 5. National Research Council (U.S.).Committee on Developmental Toxicology (2000) Appendix C: Signaling Pathways. Scientific frontiers in developmental toxicology and risk assessment. Washington, DC: National Academy Press. pp. 296–308.
- 6. Hirsh D, Oppenheim D, Klass M (1976) Development of the reproductive system of Caenorhabditis elegans. Dev Biol 49: 200–219.
- 7. Knight CG, Patel MN, Azevedo RB, Leroi AM (2002) A novel mode of ecdysozoan growth in Caenorhabditis elegans. Evol Dev 4: 16–27.
- 8. Sulston J, Hodgkin J (1988) Methods. In: Wood WB, editor. The Nematode Caenorhabditis elegans. Cold Spring Harbor, NY: Cold Spring Harbor Laboratory Press. pp. 587–606.
- 9. Lewis JA, Fleming JT (1995) Basic culture methods. Methods Cell Biol 48: 3–29.
- 10. Pulak R (2006) Techniques for analysis, sorting, and dispensing of C. elegans on the COPAS flow-sorting system. Methods Mol Biol 351: 275–286.
- 11. Boyd WA, McBride SJ, Freedman JH (2007) Effects of genetic mutations and chemical exposures on Caenorhabditis elegans feeding: evaluation of a novel, high-throughput screening assay. PLoS ONE 2: e1259.
- 12. Dong J, Boyd WA, Freedman JH (2008) Molecular characterization of two homologs of the Caenorhabditis elegans cadmium-responsive gene cdr-1: cdr-4 and cdr-6. J Mol Biol 376: 621–633.
- 13. Peterson RT, Nass R, Boyd WA, Freedman JH, Dong K, et al. (2008) Use of non-mammalian alternative models for neurotoxicological study. Neurotoxicology 29: 546–555.
- 14. Smith MV, Boyd WA, Kissling GE, Rice JR, Snyder DW, et al. (2009) A Discrete Time Model for the Analysis of Medium-throughput C. elegans Growth Data. PLoSONE XXX–XXX.
- 15. Agency for Toxic Substances and Disease Registry (1997) Toxicological Profile for Chlorpyrifos;. In: Service UPH, editor. Atlanta: US Public Health Service. 217 p.
- 16. Connors SL, Levitt P, Matthews SG, Slotkin TA, Johnston MV, et al. (2008) Fetal mechanisms in neurodevelopmental disorders. Pediatr Neurol 38: 163–176.
- 17. Eaton DL, Daroff RB, Autrup H, Bridges J, Buffler P, et al. (2008) Review of the toxicology of chlorpyrifos with an emphasis on human exposure and neurodevelopment. Crit Rev Toxicol 38: Suppl 21–125.
- 18. Slotkin TA (2004) Cholinergic systems in brain development and disruption by neurotoxicants: nicotine, environmental tobacco smoke, organophosphates. Toxicol Appl Pharmacol 198: 132–151.
- 19. Sherman JD (1996) Chlorpyrifos (Dursban)-associated birth defects: report of four cases. Arch Environ Health 51: 5–8.
- 20. Environmental Protection Agency US (2000) Chlorpyrifos revised risk assessment and agreement with registrants.
- 21. Byerly L, Cassada RC, Russell RL (1976) The life cycle of the nematode Caenorhabditis elegans. I. Wild-type growth and reproduction. Dev Biol 51: 23–33.
- 22. Akaike H (1974) A new look at the statistical model identification. IEEE Trans Autom Control AC-19: 716–723.
- 23. Boyd WA, Smith MV, Kissling GE, Freedman JH (2009) Medium- and high-throughput screening of neurotoxicants using C. elegans. Neurotoxicol Teratol.
- 24. Ruaud AF, Bessereau JL (2006) Activation of nicotinic receptors uncouples a developmental timer from the molting timer in C. elegans. Development 133: 2211–2222.
- 25. Anderson GL, Boyd WA, Williams PL (2001) Assessment of sublethal endpoints for toxicity testing with the nematode Caenorhabditis elegans. Environ Toxicol Chem 20: 833–838.
- 26. Nguyen M, Alfonso A, Johnson CD, Rand JB (1995) Caenorhabditis elegans mutants resistant to inhibitors of acetylcholinesterase. Genetics 140: 527–535.
- 27. Jameson RR, Seidler FJ, Qiao D, Slotkin TA (2006) Chlorpyrifos affects phenotypic outcomes in a model of mammalian neurodevelopment: critical stages targeting differentiation in PC12 cells. Environ Health Perspect 114: 667–672.
- 28. Sulston JE, Horvitz HR (1977) Post-embryonic cell lineages of the nematode, Caenorhabditis elegans. Dev Biol 56: 110–156.
- 29. Rand JB (2007) Acetylcholine. WormBook 1–21.
- 30. Williams PL, Dusenbery DB (1988) Using the nematode Caenorhabditis elegans to predict mammalian acute lethality to metallic salts. Toxicol Ind Health 4: 469–478.
- 31. Brenner S (1974) The genetics of Caenorhabditis elegans. Genetics 77: 71–94.
- 32. Couillault C, Pujol N, Reboul J, Sabatier L, Guichou JF, et al. (2004) TLR-independent control of innate immunity in Caenorhabditis elegans by the TIR domain adaptor protein TIR-1, an ortholog of human SARM. Nat Immunol 5: 488–494.
- 33. Furlong EE, Profitt D, Scott MP (2001) Automated sorting of live transgenic embryos. Nat Biotechnol 19: 153–156.
- 34. Gill MS, Olsen A, Sampayo JN, Lithgow GJ (2003) An automated high-throughput assay for survival of the nematode Caenorhabditis elegans. Free Radic Biol Med 35: 558–565.
- 35. Rea SL, Wu D, Cypser JR, Vaupel JW, Johnson TE (2005) A stress-sensitive reporter predicts longevity in isogenic populations of Caenorhabditis elegans. Nat Genet 37: 894–898.
- 36. Hollander M, Wolfe DA (1973) Nonparametric statistical methods. New York: Wiley.
- 37. Kleinbaum DG, Kupper LL, Muller KE (1988) Applied regression analysis and other multivariable methods. Boston: PWS-Kent Pub. Co.