Full toxicity assessment of Genkwa Flos and the underlying mechanism in nematode Caenorhabditis elegans.

Genkwa Flos (GF), the dried flower bud from Daphne genkwa Sieb. et Zucc. (Thymelaeaceae), is a well-known and widely used traditional Chinese medicine. However, we know little about the in vivo mechanism of GF toxicity. Nematode Caenorhabditis elegans has been considered as a useful toxicity assay system by offering a system best suited for asking the in vivo questions. In the present study, we employed the prolonged exposure assay system of C. elegans to perform the full in vivo toxicity assessment of raw-processed GF. Our data show that GF exposure could induce the toxicity on lifespan, development, reproduction, and locomotion behavior. GF exposure not only decreased body length but also induced the formation of abnormal vulva. The decrease in brood size in GF exposed nematodes appeared mainly at day-1 during the development of adult nematodes. The decrease of locomotion behavior in GF exposed nematodes might be due to the damage on development of D-type GABAergic motor neurons. Moreover, we observed the induction of intestinal reactive oxygen species (ROS) production and alteration of expression patterns of genes required for development of apical domain, microvilli, and apical junction of intestine in GF exposed nematodes, implying the possible dysfunction of the primary targeted organ. In addition, GF exposure induced increase in defecation cycle length and deficits in development of AVL and DVB neurons controlling the defecation behavior. Therefore, our study implies the usefulness of C. elegans assay system for toxicity assessment from a certain Chinese medicine or plant extract. The observed toxicity of GF might be the combinational effects of oxidative stress, dysfunction of intestine, and altered defecation behavior in nematodes.

Introduction

Genkwa Flos (GF), the dried flower bud from Daphne genkwa Sieb. et Zucc. (Thymelaeaceae), is widely distributed in the regions of Yangtze River and Yellow River in China. GF is a well-known traditional Chinese medicine (TCM). GF has been used for the purposes of diuretic, antitussive, expectorant, abortifacient, and antitumor for centuries [1]. In GF, a series of compounds including flavonoids and daohne diterpene esters have been identified and isolated [2]–[3]. GF or compounds from GF can be potentially used for anti-inflammation, anti-complement, anti-melanogenesis, anti-virus, and anti-leukemia [4]–[8]. Moreover, because Daphne genkwa plants can be used as the effective remedy to treat various tumors [9], some compounds have also been isolated from Daphne genkwa plants because of their antitumor activity [10]–[15].

It has been commonly recognized that Daphne genkwa is a toxic shrub [15]. Previous study has investigated the cytotoxicity of compounds from Daphne genkwa with the aid of cancer cell lines [16]. The excessive or chronic application of GF also resulted in the hepatotoxicity on animals [17]–[18]. Recently, the toxicity of daphnane-type diterpenoids extracted from GF was further examined in rat with the aid of mortality and time to death as the toxicity assessment endpoints [19]. However, so far the toxicity information on GF is still very limited. Especially, we still know little about the in vivo mechanism for GF toxicity.

Free-living nematode Caenorhabditis elegans, a thoroughly studied model animal, has been considered as a useful alternative toxicity assay system for mammalians [20]–[22]. The experimental potential of C. elegans can offer a system best suited for asking the in vivo questions [20]–[22]. C. elegans has been used in both toxicity assessment and toxicological study for many toxicants including metals [23]–[36], organic pollutants [37]–[42], and engineered nanomaterials (ENMs) [43]–[53]. It has been proven that C. elegans can be further used for toxicological study of drugs [54]–[58]. Especially, several studies have been performed on the investigations on beneficial or adverse effects of components isolated from specific plants and beneficial effects of specific Chinese medicines with the aid of C. elegans as the assay system [59]–[66].

In the present study, we employed the C. elegans assay system to perform the full in vivo toxicity assessment of raw-processed GF. Moreover, we tried to examine the possible underlying mechanism for the GF toxicity in nematodes. Our data here will be helpful for our understanding the possible underlying in vivo mechanism of GF toxicity. In addition, our study further implies the usefulness of C. elegans assay system for the assessment of adverse effects from a certain Chinese medicine or plant extract.

Results

GF Exposure at the Examined Concentrations did not Induce Lethality of Nematodes

Considering the property of long-term application for Chinese medicines, we performed the prolonged exposure for toxicity assessment of GF in nematodes. Prolonged exposure was performed from L1-larvae to young adult (Fig. S1A). Concentrations selected for GF exposure were 0.12, 0.14, 0.16, 0.18, 0.2, 0.22, and 0.24 g/mL (Fig. S1B). After prolonged exposure to the examined concentrations of GF, we did not observe the lethality of nematodes (Fig. S1B), implying that GF at the examined concentrations may be not lethal to the exposed organisms.

Effects of GF Exposure on Lifespan of Nematodes

We further investigated the effects of GF exposure on lifespan of nematodes. Lifespan is an important endpoint to reflect the long-term effects of a specific toxicant. Prolonged exposure to 0.12–0.18 g/mL of GF did not significantly alter lifespan of nematodes (Fig. 1). In contrast, prolonged exposure to 0.24 g/mL of GF significantly reduced the lifespan of nematodes (Fig. 1).

Figure 1

Comparison of lifespan in nematodes exposed to GF.

(A) Lifespan curves of nematodes exposed to GF. (B) Comparison of mean lifespans in nematodes exposed to GF. Exposures were performed from L1-larvae to young adult. GF, Genkwa Flos. Bars represent means ± S.E.M. **p<0.01.

Effects of GF Exposure on Development of Nematodes

To examine the effects of prolonged exposure to GF on development, we first investigated the body length in control and GF-exposed nematodes. Although prolonged exposure to 0.12 g/mL of GF did not noticeably influence the body length of nematodes, prolonged exposure to 0.18–0.24 g/mL of GF significantly reduced the body length of nematodes (Fig. 2A). Moreover, we observed that prolonged exposure to 0.18–0.24 g/mL of GF significantly induced the formation of abnormal vulva (Fig. 2B). Prolonged exposure to 0.12 g/mL of GF did not obviously affect the morphology of exposed nematodes (Fig. 2B). Compared with the control vulva having a slightly smooth surface, the abnormal vulva induced by GF exposure had a large protuberance (Fig. 2C).

Figure 2

Effects of prolonged exposure to GF on development of nematodes.

(A) Effects of GF exposure on body length. (B) Effects of GF exposure on percentage of nematodes with abnormal vulva. (C) Pictures showing the nematodes with abnormal vulva induced by GF. Asterisks show the positions of vulva. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. **p<0.01.

Effects of GF Exposure on Reproduction of Nematodes

In nematodes, reproductive organ is one of the important secondary targeted organs for toxicants [22], [67]–[69]. We further investigated the effects of prolonged exposure to GF on reproduction with the aid of brood size as the endpoint. Prolonged exposure to 0.12 g/mL of GF did not obviously influence the brood size of nematodes (Fig. 3A). In contrast, prolonged exposure to 0.18–0.24 g/mL of GF significantly reduced the brood size of nematodes (Fig. 3A). More interestingly, the decrease in brood size in GF exposed nematodes appeared mainly at day-1 during the development of adult nematodes (Fig. 3B). We did not observe the significant differences of brood size at day-2 or day-3 during the development of adult nematodes between control and GF exposure (Fig. 3B).

Figure 3

Effects of prolonged exposure to GF on reproduction of nematodes.

(A) Effects of GF exposure on brood size of nematodes. (B) Effects of GF exposure on brood size of day-1, day-2 and day-3 adult nematodes. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. NS, no significance. *p<0.05, **p<0.01.

Effects of GF Exposure on Locomotion Behavior of Nematodes

In nematodes, neuron may be another secondary targeted organ for toxicants [22], [42], [51], [70]. Previous studies have demonstrated that locomotion behavior is a relatively sensitive endpoint for toxicity assessment in nematodes [36], [48], [53]. We next investigated the effects of prolonged exposure to GF on locomotion behavior in nematodes. Prolonged exposure to all the examined concentrations of GF significantly decreased both head thrash and body bend of nematodes (Figs. 4A and 4B). Our data here further suggest the sensitivity of locomotion behavior for toxicity assessment in nematodes.

Figure 4

Effects of prolonged exposure to GF on locomotion behavior and development of D-type GABAergic motor neurons in nematodes.

(A) Effects of GF exposure on head thrash. (B) Effects of GF exposure on body bend. (C) Effects of GF exposure on development of D-type GABAergic motor neurons. (D) Effects of GF exposure on relative fluorescent intensity of cell bodies at ventral cord of D-type GABAergic motor neurons. (E) Effects of GF exposure on neuronal loss of D-type GABAergic motor neurons. (F) Effects of GF exposure on gap formation on ventral or dorsal cord of D-type GABAergic motor neurons in nematodes. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. **p<0.01.

GF Exposure Affects the Development of D-type GABAergic Motor Neurons in Nematodes

In C. elegans, locomotion behavior is under the control of D-type GABAergic motor neurons [71]. Prolonged exposure to 0.24 g/mL of GF obviously influenced the development of D-type GABAergic motor neurons (Fig. 4C). The severe deficits in axon development were observed in 0.24 g/mL of GF exposed nematodes (Fig. 4C). Prolonged exposure to 0.24 g/mL of GF significantly decreased the fluorescent intensity of cell bodies for ventral cord D-type GABAergic motor neurons (Fig. 4D). Moreover, prolonged exposure to 0.24 g/mL of GF noticeably induced the neuronal loss and the gap formation on both ventral and dorsal cords of D-type GABAergic motor neurons (Figs. 4E and 4F). Thus, GF exposure can potentially cause damage on development of D-type GABAergic motor neurons in nematodes.

Effects of GF Exposure on Intestinal Reactive Oxygen Species (ROS) Production in Nematodes

In nematodes, intestine is the primary targeted organ for toxicants [22], [46], [67]–[69], [72]. Previous studies have implied that the functional state of intestinal barrier is required for nematodes to protect themselves from the damage of toxicants [67]–[69]. To examine the possible mechanism explaining the GF toxicity, we investigated the effects of prolonged exposure to GF on intestinal ROS production. After prolonged exposure, GF at concentrations of 0.12–0.24 g/mL significantly induced the intestinal ROS production (Figs. 5A and 5B), implying the damage from GF exposure on intestinal development in nematodes.

Figure 5

Effects of prolonged exposure to GF on intestinal development in nematodes.

(A) Pictures showing the effects of GF exposure on intestinal ROS production. Paraquat (2 mM) treatment for 12-hr from L4-larvae was used as a positive control. Paraquat is a commonly used ROS-generator. (B) Comparison of intestinal ROS production between control and GF exposed nematodes. (C) Expression patterns of genes required for intestinal development in control and GF exposed nematodes. The results were expressed as the relative expression ratio between the targeted gene and the reference tba-1 gene. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. **p<0.01.

Alteration of Expression Patterns of Genes Required for Intestinal Development in Nematodes

Moreover, we found that prolonged exposure to 0.24 g/mL of GF significantly altered the expression patterns of some genes required for intestinal development in nematodes [73]. Although GF exposure did not influence the expression patterns of vha-6, let-413, inx-3, abts-4, gem-4, egl-8, nhx-2, par-6, act-5, par-3, ifb-2, and nfm-1 genes, GF exposure significantly increased expression levels of pkc-3, eps-8, pgp-3, and erm-1 genes and decreased expression levels of ajm-1, lin-7, dlg-1, gtl-1, pgp-1, mtm-6, and opt-2 genes (Fig. 5C, Fig. S2). In C. elegans, pkc-3 gene encodes an atypical protein kinase, eps-8 gene encodes a homolog of mouse epidermal growth factor receptor kinase substrate, pgp-1 and pgp-3 genes encode transmembrane protein, erm-1 gene encodes an ortholog of the ERM family of cytoskeletal linker, ajm-1 gene encodes a member of the apical junction molecule class, lin-7 gene encodes a protein containing a PDZ domain and an L27 domain, dlg-1 gene encodes a MAGUK protein, gtl-1 gene encodes a TRPM subfamily member of the TRP channel family, mtm-6 gene encodes a myotubularin lipid phosphatase orthologous, and opt-2 gene encodes a high-affinity, proton-coupled oligopeptide transporter (Table S1).

Effects of GF Exposure on Defecation Behavior in Nematodes

Besides the intestinal development, defecation behavior may also be an important regulator for toxicity formation of toxicants in nematodes [68]. We further investigated the effects of prolonged exposure to GF on defecation behavior with the aid of mean defecation cycle length as the assay endpoint. After prolonged exposure, GF at concentrations of 0.12–0.24 g/mL significantly increased the mean defecation cycle length (Fig. 6A), which implies the possible damage of GF on structures controlling defecation behavior or the difficulty of toxic components of GF to be excreted out of the body.

Figure 6

Effects of prolonged exposure to GF on defecation behavior and development of neurons controlling defecation behavior in nematodes.

(A) Effects of GF exposure on mean defecation cycle length. (B) Effects of GF exposure on relative size of fluorescent puncta of AVL or DVB neurons. (C) Effects of GF exposure on development of AVL neurons. (D) Effects of GF exposure on development of DVB neurons. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. *p<0.05, **p<0.01.

Damage of GF Exposure on Development of Neurons Controlling Defecation Behavior in Nematodes

In nematodes, the defecation behavior is controlled by both AVL neuron in head and DVB neuron in tail [52]. To determine whether GF exposure would cause damage on structures controlling defecation behavior, we examined the effects of prolonged exposure to GF on development of AVL and DVB neurons. After prolonged exposure, GF at the concentration of 0.24 g/mL significantly decreased the relative size of fluorescent puncta for both AVL neurons and DVB neurons in nematodes (Figs. 6B–6D). These results suggest that prolonged exposure to GF can result in the damage on neurons controlling the defecation behavior.

Molecular Basis for GF to Reduce the Lifespan in Nematodes

To determine whether certain genes playing key roles in detoxification are required for the control of GF toxicity, we examined the effects of mutations of daf-16 [74], skn-1 [75], or mdt-15 [76] gene on GF toxicity formation in nematodes. With the aid of lifespan as the endpoint, interestingly, we found that the daf-16(mu86), skn-1(zu67), and mdt-15(tm2182) mutants had the susceptible property to the GF toxicity (Fig. 7). These data confirm the possible involvement of daf-16, skn-1 and mdt-15 mediated signaling pathways in regulating the GF toxicity formation.

Figure 7

Comparison of lifespan in wild-type and mutant nematodes exposed to GF.

GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. **p<0.01.

Identification of Chemical Components in Raw-processed GF

Using the reverse phase high-performance liquid chromatography (RP-HPLC) method, we finally identified the possible chemical components in our prepared GF solution. Based on the chromatographic fingerprint, the prepared GF solution contained the chemical components of luteolin-5-O-β-D-glucoside, apigenin-5-O-β-D-glucoside, genkwanin-5-O-β-D-primeveroside, genkwanin-5-O-β-D-glucoside, genkwanin-4′-O-β-D- lutinoside, apigenin, 3′-hydroxygenkwanin, and genkwanin, and some other still unknown compounds (Fig. 8).

Figure 8

Chemical components in GF analyzed by HPLC.

1, luteolin-5-O-β-D-glucoside; 2, apigenin-5-O-β-D-glucoside, 3, genkwanin-5-O-β-D-primeveroside; 4, genkwanin-5-O-β-D-glucoside; 5, genkwanin-4′-O-β-D- lutinoside; 6, apigenin; 7, 3′-hydroxygenkwanin; 8, genkwanin. GF, Genkwa Flos.

Discussion

Previous studies have demonstrated that C. elegans can be used for toxicity assessment of metals [23]–[36], organic pollutants [37]–[42], ENMs [43]–[53], or specific components extracted from plants [62]. In this study, our data further imply that C. elegans can be used for toxicity assessment of specific Chinese medicines or plant extracts. Thus, C. elegans can be used for evaluation of both the beneficial effects [59]–[61], [63]–[66] and the adverse effects of specific Chinese medicines or plant extracts. Because most of the Chinese medicines or plant extracts still lack the detailed toxicity data, C. elegans will serve as a rapid and systematic assay system for toxicity assessment of specific Chinese medicines or plant extracts.

In the present study, we performed the full assessment of GF toxicity utilizing the in vivo C. elegans assay system. Considering the property of long-term application for GF in clinical, we performed the prolonged exposure from L1-larvae to young adult for toxicity assessment of GF. L1-larvae may be more sensitive than adults for toxicity evaluation in nematodes [25], [77]. Our data demonstrate that prolonged exposure to GF could induce the toxicity on lifespan, development, reproduction and locomotion behavior (Figs. 1–4). Especially, GF exposure induced the formation of abnormal vulva (Fig. 2C). Such a deficit was also observed in heavy metal exposed nematodes [33], [78], which suggests that the induction of abnormal vulva may be a common phenotype for adverse effects of toxicants on nematodes.

For the mechanism explaining the GF toxicity, we raised several possibilities. One of the possibilities is the induction of structural deficits caused by GF exposure. For the decrease in locomotion behavior in GF exposed nematodes, we found that prolonged exposure to GF caused the damage on development of D-type GABAergic motor neurons (Figs. 4C–4F), which specially function in the control of locomotion behavior. The second possibility is that prolonged exposure to GF may result in the damage on intestinal development. We observed the severe induction of intestinal ROS production (Figs. 5A–5B) and alteration of expression patterns of some genes required for the intestinal development (Fig. 5C). In C. elegans, mtm-6, pkc-3, pgp-1, opt-2, pgp-3, and gtl-1 genes are required for the development of apical domain of intestine, erm-1 and eps-8 are required for the microvilli development, and ajm-1, dlg-1, and lin-7 genes are required for the development of apical junction of intestine [73]. These data suggest that GF exposure may at least result in the damage on development of apical domain, microvilli, and apical junction of intestine in nematodes. In addition, these data may also imply that the response of intestinal development and function may serve as an important physiological basis for the possible adaptation of nematodes to GF. The third possibility is that GF exposure induced the increase in mean defecation cycle length, which may in turn cause the deficits in AVL and DVB neurons controlling defecation behavior and the difficulty of excretion of GF out of the body in nematodes. Moreover, the phenotypic analysis of daf-16, skn-1, and mdt-15 mutants suggests that at least daf-16, skn-1, and mdt-15 mediated signaling pathways may function as the important molecular basis for the control of GF toxicity in nematodes. Therefore, the toxicity of GF is possibly the combinational effects of oxidative stress, dysfunction of intestine, and altered defecation behavior.

Our data here suggest the potential adverse effects of GF on nematodes after prolonged exposure. These results will be helpful for our understanding and attention of the careful use of this drug in clinical. At least based on our data, the duration, dose, and developmental stage of patients should be carefully considered before use of this drug. Meanwhile, some strategies, such as modulation of the processing procedure, can be also designed and considered to reduce the possible adverse effects from GF.

In the present study, the raw-processed GF was extracted after boiling treatment. During this extraction process, some possible thermolabile molecules having the bioactivity may be broken down. Therefore, the data provided here may be not able to reflect the possible biological effects of those possible thermolabile molecules in GF. Moreover, the GF can be extracted with different strategies. Besides the water boiling, the ethanolic extraction can also be used for GF preparation. The chemical components in raw-processed GF solutions prepared with different extraction strategies may be somewhat different, which implies that the obtained data here may be not able to completely reflect the biological effects of raw-processed GF solutions prepared with the other extraction strategies on nematodes.

In conclusion, with the Chinese medicine of GF as a sample, our data here provide the evidence to indicate the value of C. elegans assay system for the in vivo toxicity assessment of specific Chinese medicines or plant extracts. After prolonged exposure, GF induced multiple toxicities on nematodes, which may be due to the combinational effects of several mechanisms including oxidative stress, intestinal dysfunction, and abnormal defecation behavior. In the prepared GF solution, many chemical components may exist. In the future, examination of the beneficial or adverse effects of specific chemical components in GF will be further helpful for our understanding and controlling the toxicity formation and the clinical use of this drug.

Materials and Methods

Plant Materials and Chemicals

The dried flower buds of Daphne genkwa Sieb et Zucc. were collected from Liuan city, Anhui province, China. No specific permissions were required for the location/activity to collect the plants, because the location does not belong to any national park or protected area of land or sea. We also confirm that the field did not involve endangered behavior to the protected species. The flower buds were authenticated, and the voucher specimen (No. 110326) has been deposited at the Herbarium in Jiangsu Key Laboratory for High Technology Research of Traditional Chinese Medicine Formulae, Nanjing University of Chinese Medicine. The raw-processed GF (24 g) was decocted 2 times with 240 mL of boiling distilled water for 2-hr. The decocted suspensions were filtered, collected, and concentrated by decompressive rotary evaporation. The prepared solutions were stored at −20°C before use. The prepared raw-processed GF can be directly used in the clinical. All the other chemicals were obtained from Sigma-Aldrich (St. Louis, MO, USA).

Strain Preparation

Nematodes used in the present study were wild-type N2, mutants of daf-16(mu86), skn-1(zu67), and mdt-15(tm2182), and transgenic strain of oxIs12[Ex(Punc-47::GFP)], originally obtained from Caenorhabditis Genetics Center. They were maintained on nematode growth medium (NGM) plates seeded with Escherichia coli OP50 at 20°C as described [79]. Age synchronous populations of L1- or L4-larvae were obtained as described previously [80]. Exposures were performed from L1-larvae to young adult in 12-well sterile tissue culture plates at 20°C in the presence of food. Exposed nematodes were used for toxicity assessment of GF with lethality, lifespan, growth, brood size, locomotion behavior, defecation, and intestinal ROS production as the endpoints.

Lethality and Growth

For lethality assay, a 1.0 mL aliquot of test solution was added to each well of tissue culture plate, which was subsequently loaded with 50 nematodes for each treatment. Following exposure, wells were observed under a dissecting microscopy, where inactive ones were scored. Nematodes were judged to be dead if they did not respond to stimulus using a small, metal wire.

Growth was assessed by the body length, which was determined by measuring flat surface area of nematodes using Image-Pro® Express software. Twenty nematodes were examined per treatment.

Lifespan Assay

In the test, the hermaphrodites were transferred daily for the first 4 days of adulthood. Nematodes were checked every day and would be scored as dead when they did not move even after repeated taps with a pick. Thirty nematodes were examined per treatment. For lifespan, graphs are representative of three trials.

Reproduction and Locomotion Behavior

Reproduction was assessed by the brood size. To assay brood size, the number of offspring at all stages beyond the egg was counted. Twenty nematodes were examined per treatment.

Locomotion behavior was evaluated by both the head thrash and the body bend. To assay head thrash, the examined nematodes were washed with K medium, and transferred into a microtiter well containing 60 µL of K medium on the top of agar. After a 1-min recovery period, head thrash, defined as a change in the direction of bending at the mid body, was counted for 1-min. To assay body bend, the examined nematodes were picked onto a second plate and scored for the number of body bends in an interval of 20-sec. A body bend was counted as a change in the direction of the part of nematodes corresponding to the posterior bulb of the pharynx along the y-axis, assuming that nematode was traveling along the x-axis. Thirty nematodes were examined per treatment.

Defecation

To assay mean defecation cycle length, individual animal was examined for a fixed number of cycles, and a cycle period was defined as the interval between initiations of two successive posterior body-wall muscle contraction steps. Thirty nematodes were examined per treatment.

Intestinal ROS Production

The examined nematodes were transferred to 1 mL of M9 buffer containing 1 µM 5′,6′-chloromethyl-2′,7′dichlorodihydro-fluorescein diacetate (CM-H2DCFDA; Molecular Probes) in 12-well sterile tissue culture plates to pre-incubate for 3-hr at 20°C in the dark. CM-H2DCFDA can specially detect the presence of various intracellular produced ROS species. The intracellular ROS can oxidate the H2DCF without fluorescence to generate the DCF with green fluorescence. The nematodes were then mounted on 2% agar pads for examination with a laser scanning confocal microscope (Leica, TCS SP2, Bensheim, Germany) at 488 nm of excitation wavelength and 510 nm of emission filter. The relative fluorescent intensities of intestines were semi-quantified, and the semiquantified ROS was expressed as relative fluorescent units (RFU). Twenty nematodes were examined per treatment.

Quantitative Real-time Polymerase Chain Reaction (PCR)

Total RNA was extracted using RNeasy Mini Kit (Qiagen). Total nematode RNA (∼1 µg) was reverse-transcribed using cDNA synthesis kit (Bio-Rad Laboratories). Quantitative reverse transcription PCR was run at the optimized annealing temperature of 58°C. The relative quantification of targeted genes in comparison to the reference tba-1 gene encoding the tubulin protein or act-1 gene encoding the actin protein was determined. The final results were expressed as the relative expression ratio (between targeted gene and reference gene). The designed primers for targeted genes and reference tba-1 or act-1 gene were shown in Table S2.

Analysis of the Axonal Degeneration and Neuronal Loss of D-type GABAergic Motor Neurons

The method was performed as described [81]. D-type GABAergic motor neurons were visualized using a transgenic strain of oxIs12 [82]. Gap numbers of ventral or dorsal cord were quantified to reflect the axonal degeneration. Neuronal loss was examined by counting the number of cell bodies in D-type GABAergic nervous system. Images were photographed and examined on the same day to avoid effects of light source variance on fluorescent intensity. Thirty nematodes were examined per treatment.

Fluorescent Images of Neurons Controlling Defecation Behavior

The fluorescent images of AVL and DVB neurons controlling defecation behavior were captured with a Zeiss Axiocam MRm camera on a Zeiss Axioplan 2 Imaging System using SlideBook software (Intelligent Imaging Innovations). Images were acquired with a Quantix cooled charge-coupled device (CCD) camera, and illumination was provided by a 175 W xenon arc lamp and GFP filter sets. The relative sizes of fluorescent puncta for cell bodies of AVL and DVB neurons were measured as the maximum radius for assayed fluorescent puncta. Twenty nematodes were examined per treatment.

Analysis of Chemical Components of Raw-processed GF

Before analysis of chemical components of GF, we added 600 µL methanol to 200 µL prepared GF, and then the suspensions were centrifugated for 10-min at 13000 rpm. The RP-HPLC method was applied to establish the chromatographic fingerprint. The separation was performed on a Elite C18 column with a mobile phase composed of methanol (A) and 0.25% acetic acid (B). Gradient elution condition was 0-min, 20% (A); 30-min, 60% (A); 45-min, 100% (A); and 50-min, 20% (A). The column temperature was set at 30°C and the flow rate was 1.0 mL/min. The detective wavelength was set at 260 nm. The injection volume was 10 µL. According to the HPLC data, the main components of prepared GF were determined.

Statistical Analysis

All data in this article were expressed as means ± standard error of the mean (S.E.M.). Graphs were generated using Microsoft Excel (Microsoft Corp., Redmond, WA). Statistical analysis was performed using SPSS 12.0 (SPSS Inc., Chicago, USA). Differences between groups were determined using analysis of variance (ANOVA). Probability levels of 0.05 and 0.01 were considered statistically significant.

Prolonged exposure to GF did not induce lethality in nematodes. (A) Schematic drawing showing the prolonged exposure to GF. (B) Effects of GF exposure on lethality. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M.

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Expression patterns of genes required for intestinal development in control and GF exposed nematodes. The results were expressed as the relative expression ratio between the targeted gene and the reference act-1 gene. GF, Genkwa Flos. Exposures were performed from L1-larvae to young adult. Bars represent means ± S.E.M. **p<0.01.

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Information on genes required for intestinal development in

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Primers used for quantitative real-time polymerase chain reaction (PCR).

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