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Yim, Kim, and Kim: Acute toxicity assessment of Osthol content in bio-pesticides using two aquatic organisms



This study focused on the assessment of acute toxicity caused by Osthol, a major component of environment-friendly biological pesticides, by using two aquatic organisms.


The assessment of acute toxicity caused by Osthol was conducted in Daphnia magna and by examining the morphological abnormalities in Danio rerio embryos.


The median effective concentration value of Osthol in D. magna 48 hours after inoculation was 19.3 μM. The median lethal concentration of D. rerio embryo at 96 hours was 30.6 μM. No observed effect concentration and predicted no effect concentration values of Osthol in D. magna and D. rerio were calculated as 5.4 and 0.19 μM, respectively. There was an increase in the morphological abnormalities in D. rerio embryo due to Osthol over time. Coagulation, delayed hatching, yolk sac edema, pericardial edema, and pigmentation were observed in embryos at 24–48 hours. Symptoms of scoliosis and head edema occurred after 72 hours. In addition, bent tails, ocular defects, and symptoms of collapse were observed in fertilized embryo tissue within 96 hours. Ocular defects and pigmentation were the additional symptoms observed in this study.


Because Osthol showed considerable toxicity levels continuous toxicity evaluation in agro-ecosystems is necessary when bio-pesticides containing Osthol are used.


The wide use of agricultural pesticides to increase farm products has created serious problems throughout the world, such as environmental destruction and degradation of ecosystems. Agricultural pesticides directly affect soil microbes and enzymatic activities, thereby leading to negative impacts on the pH, Eh, and nitrogen metabolism in soil [1].
In recent years, Organization for Economic Cooperation and Development (OECD) countries including South Korea have begun to take an interest in eco-friendly agricultural policies and well-being. Accordingly, the study and development of bio-pesticides for eco-friendly agriculture has become a priority. Biopesticides contain to biologically active substances to prevent various diseases and repel harmful insects or their commercialized biological products sold in markets.
According to the Korea Rural Economic Institute [2], the biopesticide market will amount to 3 trillion 873.2 billion sales in 2015, when agricultural pesticides with low pesticide certification system will be abolished, if some of them are replaced with pesticide-free products or organic products. It will increase to 7 trillion 474.9 billion sales in 2020, which is 20% of the entire farm product market. While agricultural pesticides take 7-10 years to develop, bio-pesticides take around 3 years, and development costs are lower than those for agricultural pesticides.
However, there are disadvantages in the use of bio-pesticides. Their effect appears late, short-lived, and diminishes when they are not used at the right time. Furthermore, these products are costly.
Nevertheless, the study and development of bio-pesticides a must continue due to their eco-friendliness, lack of chemical-resistance, insurance of safe agricultural production, and usage of natural resources as well as promotion of safe eco-systems. To comply with the current need, a bio-pesticide (product name: SSGRI), which contains a mixture of Camphor and Osthol as the main ingredients, was developed.
Hedge parsley, called Torilis japonicas, is a plant that contains a large amount of Osthol and grows in South Korea, Taiwan, China, Ussuri River, Africa, Kavkaz, and Europe. It grows in grassland to heights of 30–70 cm. Its fresh sprout is an edible vegetable and its fruit is used as an astringent, having anti-inflammatory and pesticidal properties (Figure 1). The main ingredients of its leaf include pinene, camphene, bornyl isovalerate, iso-borneol, and Osthol. In addition, Osthol is known to be effective in the treatment of pruritus genitalium, vulvar tumors, and postnatal dyslochia, as well as in the promotion of vitality [3-5].
In a previous study, our research team assessed the effects of acute exposure to Camphor [6]. In the present study, we review the effects of acute toxicity of Osthol using two aqua-organisms. Acute toxicity will be assessed using water flea fatality, swimminginhibition acute toxicity (median effective concentration [EC50]), and fry fatality (median lethal concentration [LC50]) of Danio rerio, and the morphological abnormalities induced by bio-pesticides on D. rerio embryo will be investigated. In addition, the impacts of toxicity will be compared, No observed effect concentration (NOEC) and predicted no effect concentration (PNEC) [7] will be drawn, and a stable concentration range for use on farmland eco-systems will be proposed through the assessment of acute toxicity on two organisms.

Materials and Methods

Structure and Physiochemical Characteristics of Osthol

Osthol (Santa Cruz Biotechnology, Dallas, TX, USA; GC level), extracted from Cnidii Fructus, Torilis Fructus, has a molecular weight (MW) of 244.29, octanol-water partition coefficient of 3.45, and a low water solubility but high solubility in ethanol. The structure is shown in Figure 2. The concentration of Osthol reagent used in the present research is ≥98.0%.

Rearing Conditions of Target Species for Toxicity Assessment

D. magna

D. magna was distributed from a chemical toxicity research institute and was cultured in accordance with OECD guideline 202 methods [8]. The rearing condition was set to pH 7.5±0.2, temperature of 20±1°C and photoperiod of 16:8-hour light/dark (L/D). For food, 7–10×107 cells/L of Chlorella vulgaris was provided every day. Rearing water was changed three times a week, and the number of female parents was set to 10/L.

D. rerio

The D. rerio used in acute fish toxicity assessment was distributed from Kyungpook National University. Rearing conditions were set to a temperature of 28±1°C and photoperiod of 16:8-hour L/D; rearing water was dissolved with 0.065 g/L of sodium bicarbonate (Dae Jung Chemicals, Siheung, Korea; extra pure level), and the pH was set to pH 7.5±0.2 with 12% sodium phosphate monobasic anhydrous (Dae Jung Chemicals; extra pure level) solution, while the conductivity was set to 0.39–0.43 mS/ cm with 0.16 g/L of sea salt (Aquarium Systems, France). As for food small tropical fish feed (Guppy BOb; Jeil Feed, Daejeon, Korea) was provided 3 times a day, and Ocean Star International Brine Shrimp (Snowville, UT, USA) was provided once a week.

Toxicity Assessment Method

Preparation of toxicity substance

For the toxicity assessment, Osthol (MW: 244.29; 98.0%), GC grade reagent was purchased from Santa Cruz Biotechnology (GC level). As a solvent for Osthol, ethanol (Junsei Chemicals; extra pure level) was used. Osthol 0.25 g was dissolved in ethanol, and diluted to obtain a 50 mL stock solution of 0.02 M. To adjust the concentration for each evaluation, the stock solution was diluted with culturing seawater. When dissolved, Osthol becomes alkaline. For this reason, we adjusted all solutions to pH 7.5±0.2 (the same as that of control group) at all concentrations.

Acute Toxicity Assessment of D. magna

The individuals D. magna used in the test were young, healthy individuals aged less than 24 hours. Osthol were prepared in beakers at concentrations of 2.5, 5.0, 10.0, 20.0, and 40.0 μM; 10 D. magna were placed in each beaker. During the experimental period, oxygen and food were not provided. Also, death and immobilization were observed between 24 and 48 hours. All experiments were repeated three times, and SigmaPlot version 12.0 (Systat Software, Chicago, IL, USA) was used for statistical evaluations. The pH of the 40.0 μM Osthol solution was 0.4 higher than that of the control group; hence, we adjusted all concentrations to pH 7.5±0.2 to match the control.

Egg Production of D. rerio

During spawning, male and female D. rerio are easily distinguishable, because male D. rerio have an orange body with a silver belt whereas female D. rerio have a red body and swollen abdomen.
The night before the spawning, male and female D. rerio in a 2:1 ratio were transferred to the darkened mating cage. During the copulation, spawning, and fertilization, light was emitted and eggs were produced within 30 minutes. D. rerio tends to eat their eggs; hence, and the adults were separated from the eggs [9]. The collected eggs were washed with methylene blue solution and egg water. The fertilized and unfertilized eggs were separated using an optical microscope (Eclipse E200; Nikon, Tokyo, Japan), and only the fertilized eggs were used for further observations.

Acute toxicity Assessment and Embryo Toxicity Assessment of D. rerio

Osthol was prepared in 2.5, 5.0, 10.0, 20.0, and 40.0 μM concentrations by diluting with the D. rerio rearing water. Then, 2.5 mL of Camphor was put in each concentration in 24-well plates, and three sets of experiments were repeated 10 times. During the test, the temperature was set to 28±1°C, pH was set to 7.5±0.2, conductivity was set to 0.4 mS/cm, and photoperiod was set to 16/8-hour L/D. Individuals that died or showed morphological abnormalities were observed with a microscope and numbered within 0–96 hours, for every 24 hour, and statistical analyses were carried out through SigmaPlot version 12.0 Embryo toxicity was assessed with 30 replicates per concentration, and the incidents of every abnormality were cumulatively recorded and expressed as a percentage. As there were cases where multiple incidents occurred for a single embryo, the total amount could be over 100%.

Estimation of No Observed Effect Concentration and Predicted No Effect Concentration

If only limited toxicity data were obtained from the toxicity assessment of chemical substances in the OECD, a constant assessment factor was used in each extrapolation stage to predict the PNEC of the ecosystem. The acute toxicity assessment results for the two species of subject organisms were adjusted to a constant assessment factor of 100 to derive the PNEC and NOEC [7,10].


Acute Toxicity Assessment of D. magna

D. magna were not affected by toxicity below 5.0 μM after 48 hours; however, at 10.0 μM Osthol led to fatalities and inhibited swimming. At the highest concentration of 40.0 μM, the survival rate was 6.7%, exhibiting very high toxicity. In this assessment, in which the impact of solvent was excluded, the survival rate in 0.188% ethanol was 90.0%, showing almost no toxicity. Meanwhile, the EC50 of D. magna after 48 hours was 19.3 μM (Figure 3A).

Egg Production of D. rerio

Osthol was toxic to D. rerio embryos and increased the fatality rate at concentrations above 5.0 μM. The amount of ethanol contained in Osthol 40.0 μM was 0.188%. The toxic effect of the solvent on fertilized D. rerio eggs did not appear as it did in D. magna. LC50 value of Osthol’s exposure to D. rerio embryo for 96 hours was 30.6 μM (Figure 3B).

Effects of Elapsed Time on Fertilized Eggs of D. rerio

Twenty-four Hours after Fertilization

When Osthol at concentration of 5-40 μM was prepared and exposed to D. rerio, 24 hours after fertilization, congelation (C) of 10.0, 10.0, and 53.3% occurred at 10.0, 20.0, and 40.0 μM, respectively. However, C did not occur at concentrations below 5.0 μM. Morphological abnormalities of D. rerio 24 hours after fertilization are shown in Figure 4 and Table 1. It is important to note that congelation at 40.0 μM was 5.3-fold higher than at 20.0 μM, showing a significant increase. A mechanism that promoted significant C emerged above certain concentrations (Figure 3C).

Forty-eight Hours after Fertilization

Forty-eight hours after fertilization, 10% C occurred at 10.0 μM, 10% C and 3.3% tail edema (TE) at 20.0 μM, and 53.3% C and 6.7% TE at 40.0 μM. The morphological abnormalities of D. rerio, 48 hours after fertilization, are shown in Figure 4 and Table 1.

Seventy-two Hours after Fertilization

Seventy-two hours after fertilization, there appeared C: 13.3% at 10.0 μM, C 13.3%, pericardial edema (PE) 33.3% and TE 36.7% at 20.0 μM, and C 60.0%, yolk sac edema (YSE) 10.0%, PE 50.0%, TE 36.7%, Head edema (HE) 3.3% and bent spine (BS) 3.3% at 40.0 μM. The morphological abnormalities of D. rerio, 72 hours after fertilization, are shown in Figure 4 and Table 1.

Ninety-six Hours after Fertilization

Ninety-six hours after fertilization, C, PE and TE at 10.0 and 20.0 μM remained constant at the level observed at 72 hours, with no morphological abnormalities observed at increasing concentrations. Morphological abnormalities other than TE, bent spine (BS), and collapse of fertilized egg tissue (NF) at 40.0 μM was consistent with those observed 72 hours after fertilization. However, bent tail (BT), BS, and NF were 40.0, 13.3, and 13.3%, respectively, which were greater than those at 72 hours post fertilization (Figure 5). The morphological abnormalities of D. rerio, 96 hours after fertilization, are shown in Figure 4 and Table 1.

Morphological Abnormality Changes with Concentration and Time

Osthol was prepared at various concentrations and the types of abnormalities present 96 hours after fertilization were observed. No morphological abnormalities were found below 5.0 μM. However, 13.3% C occurred at 10.0 μM concentration; C, PE and TE occurred in 13.3, 33.3, and 36.7% of cases, respectively, at 20.0 μM; and C, YSE, PE, TE, HE, BT, and abnormalities where the form of the fertilized egg tissue showed symptoms of NF occurred at 60.0, 10.0, 50.0, 40.0, 3.3, 13.3, and 13.3%, respectively, at 40.0 μM (Figure 4 and Table 1).
Edema accompanied by hemorrhage was observed as a morphological abnormality. According to a previous study reported by Ko et al. [11], Osthol lowers blood pressure by dilating the thoracic aorta in rat, leading to a decrease in systolic blood pressure. In our study, it is thought that there was expansion and destruction of immature vessels in the emerging process of fertilized D. rerio eggs, thereby resulting in bleeding accompanied by edema. Although the reason was not clear, certain toxicity was observed to occur, which destroyed the vascular system in D. rerio and led to edema as a consequence of bleeding.

Change in the Congelation Rate

While C of fertilized D. rerio eggs by Osthol was not observed below 5.0 μM, it was increased at 10.0, 20.0, and 40.0 μM up to 72 hours, and was then maintained a constant level until 96 hours (Figure 3C). Such fertilized eggs did not hatch and died.
Calcium (Ca) has a main role in information transmission and controls various functions that are essential for sustaining life [12]. Division and multiplication of fertilized eggs occurs following the influx of Ca, and an increase of Ca in cells can lead to death. Cell membranes have Ca channels that control the influx of Ca into cells, a Ca pump, which removes Ca from cells, and a Ca+/Na+ exchange pump, which removes Ca by exchanging it with Na, and thereby maintaining intracellular Ca at a constant level.
Chiou et al. [13] reported the inhibitory effect of Osthol on the influx of Ca. HE confirmed that C occurred in D. rerio embryos at concentrations over 10.0 μM, in a manner that was not dependent on concentration. Although there is no clear conclusion for its reason, its possibility cannot be excluded.

Change in Hatchability

While the hatching rate of the control group was high at 96.7% after 48 hours fertilization, the hatching rates at 2.5, 5.0, 10.0, 20.0, and 40.0 μM were 56.7, 50.0, 43.3, 33.3, and 26.7%, respectively, showing that the hatching rate decreased with increasing concentration. However, the hatching rates at 2.5, 5.0, and 10.0 μM were 100, 100, and 86.7%, respectively, after 72 hours, and maintained until 96 hours after fertilization.
Considering that the normal hatching time of the control group was after 48 hours, the hatching time was delayed significantly. In addition, the hatching rates at 20.0 and 40.0 μM after 72 hours were 86.7 and 40.0%, respectively, which were lower than those at low concentrations. Hatching rates after 96 hours fell to 76.7 and 26.7%, which were lower than those at 72 hours. The reason is that although they hatched after 72 hours, they subsequently died due to toxicity, thus resulting in an overall lower hatching rate (Figure 3D).

Safe Application Concentration of Bio-pesticide

This study conducted an acute toxicity assessment of Osthol using D. magna and D. rerio. According to the result, D. magna was more sensitive to the effects of toxicity than was D. rerio. The EC50 of D. magna at 48 hours of exposure was 19.3 μM, which corresponds to 1,036-fold when converting into the dilution magnification value of the bio-pesticide. This result means that the EC50 was 1,000-fold of the actual pesticide spraying concentration. Meanwhile, since the test was conducted on two organisms, an uncertainty evaluation factor of 100 was applied to the EC50 of water fleas, which showed sensitivity to toxicity, and then PNEC was drawn. PNEC at this point was predicted to be 0.19 μM (105,263-fold diluted water).
In other words, when Osthol exists below 19 μM in an ecosystem, toxicity cannot be predicted. In addition, since the NOEC value was assessed to be 5.4 μM (3,704-fold), it can be said that no toxic effect was observed below this concentration. Accordingly, based on the results stated above, it can be concluded that a significant toxic effect may occur when sprayed on sites at 1,000-fold dilution (Table 2).


The assessment of acute toxicity of Osthol to two organisms was conducted. As a result, the EC50 of its exposure to D. magna for 48 hours was 19.3 μM (1,036-fold diluted water), and the LC50 of its exposure to D. rerio embryos for 96 hours was 30.6 μM (654-fold diluted water). NOEC and PNEC of Osthol were 5.4 μM (3,704-fold diluted water), 0.19 μM (105,263-fold diluted water), respectively. At 48 hours, C, a morphological abnormality of D. rerio, increased at concentrations above 10.0 μM, and was maintained for 72 hours.
TE was found in hatching-delayed embryo in concentrations above 20.0 μM. Seventy-two hours after fertilization, PE, YSE, HE, and BT abnormalities were discovered above 20.0 μM. Ninety-six hours after fertilization, abnormality manifest as NF appeared, and bleeding occurred together at the place where edema appeared. Since the EC50 of Osthol was 19.3 μM, and the site spraying concentration of 1,000-fold diluted water (20.0 μM) are similar, it is predicted that significant toxic effects will appear at the sprayed sites. In our previous study, NOEC of Camphor was 55.2 μM (7,156-fold diluted water based on the guidelines on bio-pesticides), and PNEC was 3.95 μM (100,000-fold diluted water).
Dilution magnifications corresponding to the EC50 were 1,000-fold when compared with the EC50 (395.0, μM) of Camphor and 1,000-fold of the dilution magnification value (395.0 μM). However, when bio-pesticide SSAGRI was assessed using D. magna, it showed very high toxicity, causing 100% death at 500-fold diluted water and 1,000-fold diluted water, which are spraying standards. Main ingredients of SSAGRI include Camphor 6.25%, Osthol 0.5%, surfactant 5% and grapefruit seed extract 5%. This indicates that the mixture of several ingredients can cause toxicity. To clarify this, further studies on the difference between each ingredient’s toxicity and that of the mixture are required.


We sincerely thank the Ministry of Trade, Industry and Energy who supported the present research, as part of a Program Sponsoring the Leading Businesses in the Honam Economic Region (no. R0001955).

Conflict of interest

The authors have no conflicts of interest with material presented in this paper.


1. Lee KS. Evaluation on the effects of pesticide residues to agroecosystem in Korea. Korean J Environ Aagric 1997;16(1):80-93 (Korean).

2. Jeong HK, Moon DH. Response strategy to the abolishment of low-pesticide agricultural product certification. Seoul: Korea Rural Economic Institute; 2013. p. 88 (Korean).

3. Matsuda H, Ido Y, Hirata A, Ino Y, Naruto S, Amamiya T, et al. Antipruritic effect of Cnidii Monnieri Fructus (fruits of Cnidium monnieri CUSSON). Biol Pharm Bull 2002;25(2):260-263.
crossref pmid
4. Matsuda H, Tomohiro N, Ido Y, Kubo M. Anti-allergic effects of cnidii monnieri fructus (dried fruits of Cnidium monnieri) and its major component, osthol. Biol Pharm Bull 2002;25(6):809-812.
crossref pmid
5. Yamahara J, Kozuka M, Sawada T, Fujimura H, Nakano K, Tomimatsu T, et al. Biologically active principles of crude drugs. Anti-allergic principles in “Cnidii monnieri”. Chem Pharm Bull (Tokyo) 1985;33(4):1676-1680.
crossref pmid
6. Yim EC, Kim HJ, Kim SJ. Acute toxicity assessment of camphor in biopesticides by using Daphnia magna and Danio rerio. Environ Health Toxicol 2014;29: e2014008.
crossref pmid pmc
7. van Leeuwen CJ, Vermeire T. Risk assessment of chemicals: an introduction. 2nd ed. Dordrecht: Springer; 2007. p. 326-340.

8. Organization for Economic Cooperation and Development. Test No. 202: Daphnia sp. acute immobilisation test. 2004. [cited 2014 Jun 20]. Available from: http://www.oecd-ilibrary.org/docserver/ download/9720201e.pdf?expires=1417618460&id=id&accname =guest&checksum=BD88013F235EB83D42D7764D3EF51C7E.

9. Lammer E, Carr GJ, Wendler K, Rawlings JM, Belanger SE, Braunbeck T. Is the fish embryo toxicity test (FET) with the zebrafish (Danio rerio) a potential alternative for the fish acute toxicity test? Comp Biochem Physiol C Toxicol Pharmacol 2009;149(2):196-209.
crossref pmid
10. Yim EC, Shin JJ, Park IT, Han HK, Kim SW, Cho H, et al. Acute toxicity assessment of new algicide, thiazolidinedione derivative (TD53) to marine ecosystem. Korean Soc Biotechnol Bioeng J 2011;26(1):7-12 (Korean).
11. Ko FN, Wu TS, Liou MJ, Huang TF, Teng CM. Vasorelaxation of rat thoracic aorta caused by osthole isolated from Angelica pubescens. Eur J Pharmacol 1992;219(1):29-34.
crossref pmid
12. Huzita T. Wonders of the new calcium: calcium to support the future of the human race. Tokyo: Kodansha; 1996. p. 208 (Japanese).

13. Chiou WF, Huang YL, Chen CF, Chen CC. Vasorelaxing effect of coumarins from Cnidium monnieri on rabbit corpus cavernosum. Planta Med 2001;67(3):282-284.
crossref pmid

Figure 1.
Images of flowers, leaves and fruit of Torilis japonica Decandolle (from left to right).
Figure 2.
Chemical structure of Osthol.
Figure 3.
Acute toxicity of Osthol to D. magna (A) and D. rerio embryo (B) at 96 hours and the congelation for each observation time by Osthol (C), hatching rate for each observation time by Osthol (D), (n=30). EC50, median effective concentration; LC50, median lethal concentration.
Figure 4.
Image summary of morphological abnormalities of D. rerio embryo by Osthol. C, congelation; YSE, yolk sac edema; PE, pericardiac edema; TE, tail edema; BS, bent spine; HE, head edema; NF, collapse symptoms of fertilized embryo tissue.
Figure 5.
Rate of congelation (C), yolk sac edema (YSE), pericardiac edema (PE), tail edema (TE), head edema (HE), bent spine (BS) and collapse symptoms of fertilized embryo tissue (NF) caused by Osthol at 96 hours (n=30).
Table 1.
Effect degree on the abnormal morphological symptoms of D. rerio embryo after exposure to Osthol
Concentration (μM) Symptoms (%)
Yolk sac edema
Pericardiac edema
Tail edema
Head edema
Bent spine
Collapse symptoms of fertilized embryo tissue
24 48 72 96 24 48 72 96 24 48 72 96 24 48 72 96 24 48 72 96 24 48 72 96 24 48 72 96
10 10.0 10.0 13.3 13.3 - - - - - - - - - - - - - - - - - - - - - - - -
20 10.0 10.0 13.3 13.3 - - - - - - 33.3 33.3 - 3.3 36.7 36.7 - - - - - - - - - - - -
40 53.3 53.3 60.0 60.0 - - 10.0 10.0 - - 50.0 50.0 - 6.7 36.7 40.0 - - 3.3 3.3 - - 3.3 13.3 - - - 13.3
Table 2.
The values of EC50 or LC50, NOEC and PNEC of Osthol obtained from the acute toxic assessment using D. magna and D. rerio
Ingredient Species E(L)C50 (μM) (dilution rate) NOEC (μM) (dilution rate) Factor PNEC (μM) (dilution rate)
Osthol D. magna 19.3 (×1,036) 5.4 (×3,704) 100 0.19 (×105,263)
D. rerio 30.6 (×654) 5.4 (×3,704)

EC50, median effective concentration; LC50, median lethal concentration; NOEC, no observed effect concentration; PNEC, predicted no effect concentration.

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