The pinewood nematode
Bursaphelenchus xylophilus
(Nematoda: Parasitaphelenchidae) poses a serious threat to pine forests in Europe and East Asia, leading to a debilitating pine wilt disease. Infected pine trees in Korea are generally fumigated or crushed to small wood chips after felling. Although pine wilt disease often recurs in pest management sites, there are no adequate means to monitor the effectiveness of pest control measures in those sites. Recently, a male-produced aggregation pheromone, 2-(undecyloxy)ethanol, was shown to be useful for attracting several
Monochamus
species, which are vectors for the pinewood nematodes. In this study, we investigated the abilities of 2-(undecyloxy)ethanol at three different doses (175, 350, and 700 mg), as well as host plant volatiles (α-pinene and ethanol), to attract
M. alternatus
(Coleoptera: Cerambycidae) at a pine forest in Pohang, Korea where infected pine trees had been cut down and fumigated. Twenty-seven
M. alternatus
were captured in cross-vane panel traps made of polyethylene terephthalate bottles and acrylic sheets. The results indicate that a high dose of 2-(undecyloxy)ethanol (700 mg per trap) is the most effective for attracting
M. alternatus
. The aggregation pheromone could be used to monitor the effectiveness of pest control measures as well as
M. alternatus
populations.
Introduction
Pine wilt disease, which blocks the circulation of water and nutrients in pine trees, is caused by the pinewood nematode
Bursaphelenchus xylophilus
(Nematoda: Parasitaphelenchidae). Pinewood nematodes, native to North America, were accidentally introduced to Japan around 1905
[10]
, later spreading to China, Taiwan, and Korea. The nematodes were also detected in Europe (Portugal) in 1999
[16]
. In Korea, where pine forest occupies approximately 23% of the land, pine wilt disease poses a serious threat to forest ecosystems ever since its first occurrence in 1988
[7
,
14]
. The Japanese red pine (
Pinus densiflora
), black pine (
P. thunbergii
Parl.), and Korean white pine (
P. koraiensis
) are all affected by pine wilt disease
[14]
. Nationwide efforts have been made to suppress the spread of pine wilt disease including fumigation or crushing of infected pine trees after cutting down, aerial spraying of insecticide, as well as injection of insecticide into pine tree trunks
[7
,
14]
. However, no adequate means of monitoring pine wilt disease at pest management sites have been devised instead of detection of newly infected pine trees.
In East Asia, longhorn pine sawyer beetles,
M. alternatus
and
M. saltuarius
(Coleoptera: Cerambycidae), are primary vectors of pinewood nematodes
[1
,
11]
.
Monochamus alternatus
is found mainly in the southern part of Korea with an annual mean temperature >13℃, whereas
M. saltuarius
is found in the mid-to-northern part of the country with an annual mean temperature <13℃
[8]
. Host plant volatiles such as α-pinene and ethanol are known to attract
Monochamus
species
[4
,
5]
. Recently, 2-(undecyloxy)ethanol was identified as a male-produced aggregation pheromone of both
M. galloprovincialis
[13]
and
M. alternatus
[15]
. The hydroxyether structural motif found in 2-(undecyloxy)ethanol is considered to be conserved among many pheromones of Cerambycidae species
[3]
Attraction to aggregation pheromones is strongly synergized by host plant volatiles
[2
,
12
,
13
,
15]
.
In this study, we investigated the abilities of 2-(undecyloxy) ethanol along with the host plant volatiles α-pinene and ethanol to attract
M. alternatus
at a pine forest in Pohang, Korea. We used three different doses of 2-(undecyloxy)ethanol (175, 350, and 700 mg), whereas a single dose of 2-(undecyloxy)ethanol in the range of 25-95 mg per trap was used in other studies
[9
,
12
,
13
,
15]
. To increase the surface area of the pheromone mixture, a super-absorbent polymer based on polyacrylic acids and water were added to the solution of 2-(undecyloxy)ethanol and host plant volatiles. As an alternative to commercial cross-vane panel traps or multi-funnel traps, we made cross-vane panel traps using polyethylene terephthalate (PET) bottles and acrylic sheets. Here, we report that a high dose of 2-(undecyloxy)ethanol (700 mg per trap) is the most effective for attracting
M. alternatus
at a pest management site in Korea.
Materials and Methods
- Synthesis of 2-(undecyloxy)ethanol
The aggregation pheromone 2-(undecyloxy)ethanol was synthesized using the microwave-assisted organic synthesis technique.
((2-(Undecyloxy)ethoxy)methyl) benzene : 2-(benzyloxy) ethanol (0.50 g, 3.3 mmol) in 2 ml of N,N-dimethylformamide was added to sodium hydride (0.16 g, 6.6 mmol), and the reaction mixture was stirred for 5 min at 25℃. A microwave tube filled with the above mixture and 1-bromoundecane (0.85 g, 3.6 mmol) was heated in the microwave reactor at 100 W power and 80℃ for 10 min. After removal of solvent
in vacuo
, the residue was treated with ethyl acetate and washed with water and saturated aqueous sodium chloride solution. The obtained organic layer was dried over anhydrous sodium sulfate and concentrated
in vacuo
. The residue was purified by flash column chromatography over silica gel using hexane:ethyl acetate (20:1 and then 9:1) mixtures as eluents to obtain 0.72 g of product at 72% yield.
1
H NMR (CDCl
3
, 400MHz) δ (ppm): 7.35-7.23(m, 5H), 4.57(s, 2H), 3.60(s, 4H), 3.45(t,
J
=6.8 Hz, 2H), 1.59(quint,
J
=6.9 Hz, 2H), 1.30-1.26(m, 16H), 0.88(t,
J
=6.6 Hz, 3H).
2-(undecyloxy)ethanol: ((2-(undecyloxy)ethoxy)methyl) benzene (0.72 g, 2.3 mmol) in 10 ml of ethanol was added to a catalytic amount of palladium on activated carbon (10%), and the resulting mixture was stirred for 5 hr under a hydrogen gas atmosphere. After the reaction mixture was filtered with celite, the filtrate was concentrated
in vacuo
. The residue was purified by flash column chromatography over silica gel using hexane:ethyl acetate (5:1 and then 3:1) mixtures as eluents to obtain 0.37 g of product at 73% yield.
1
H NMR (CDCl
3
, 400M Hz) δ (ppm): 3.73 (q,
J
= 5.1 Hz, 2H), 3.53 (t,
J
= 4.6 Hz, 2H), 3.47 (t,
J
= 6.6 Hz, 2H), 2.28 (t,
J
= 6.0 Hz, 1H), 1.59 (quint,
J
= 7.0 Hz, 2H), 1.30-1.26 (m, 16H), 0.88 (t,
J
= 6.8 Hz, 3H).
13
C NMR (CDCl
3
, 100M Hz) δ (ppm): 70.86, 70.46, 60.76, 30.92, 28.63, 28.51, 28.35, 25.10, 21.69, 13.10.
- Construction of cross-vane panel traps
Cross-vane panel traps were constructed using 2-liter clear PET bottles and acrylic sheets as shown in
Fig. 1
. A PET bottle was cut into three pieces. The upper part, which serves as a funnel in an upside-down position, was assembled to the base part (capacity 1.2 liters). The cover and cross-vane panel were constructed using acrylic sheets.
Schematic diagram of cross-vane panel trap made of PET bottle and acrylic sheets. A 2-liter PET bottle was cut into three pieces. The upper part, which serves as a funnel in an upside-down position, was assembled to the base part. The capacity of the base part is 1.2 liters. The cross-vane panel and cover were made of acrylic sheets.
- Superabsorbent polymer-based pheromone lure
(±)-α-Pinene, ethanol, and isopropanol were purchased from Sigma (St. Louis, MO, USA). Superabsorbent polymer based on polyacrylic acid was purchased from a local perfume store. To increase the surface area of the pheromone mixture, α-pinene, ethanol, and 2-(undecyloxy)ethanol were mixed in a 50 ml conical tube, followed by addition of polyacrylic acid-based superabsorbent polymer (0.45 g) and water (approximately 27 ml). The volume of water was adjusted to maintain a ratio of pheromone mixture to water of 1:4. The lure was kept at room temperature overnight before use.
- Field bioassay
A field experiment was carried out at a pine forest in Pohang, Korea for 2 weeks from June 24, 2014 to July 7, 2014 within 36°08'87''N, 129°33'03''E and 36°09'37''N, 129°31'88''E (
Fig. 2
). Black pine (
Pinus thunbergii
Parl.), native to Korea and Japan, was predominant at this site. The area was previously affected by pine wilt disease, wherein the infected pine trees had been cut down and fumigated using metham sodium
[7
,
14]
. However, as control methods such as fumigation or crushing to small wood chips after felling of infected trees cannot remove all infected trees, including their branches, we speculate that there are still some living
M. alternatus
there. Daily monitoring of
M. alternatus
in an outdoor netted cage at Pohang since 2008 showed that
M. alternatus
emerges from the logs of infected pine trees on average on May 27, and its cumulative emergence ratio reaches 50% on June 21 (Gyeongsangbuk-do Forest Environment Research Institute, unpublished data). These data are consistent with the observations of Kim et al., who showed that the emergence of
M. alternatus
in Jinju, Korea occurs on average on May 15, and a 50% cumulative emergence ratio is reached at mid-June
[6]
. As Jinju is located 160 km south of Pohang, the emergence of
M. alternatus
in Jinju is 12 days earlier than Pohang.
Arrangement of traps at the experiment site at a pine forest in Pohang, Korea. Twenty traps were allocated into four blocks of five treatments. Traps were randomly installed in each block, 50 m between traps, and 1.2 m high above the ground. Blocks 1 to 4 are denoted as I~IV.
Twenty traps were allocated in four blocks of five treatments (
Fig. 2
). Block 1 was located near the campus of Sunlin College while block 2 was close to a cemetery. Blocks 3 and 4 were close to a paddy field. As host plant volatiles α-pinene and ethanol (H) were reported to attract
Monochamus
species
[4
,
5]
, we used three different doses of 2-(undecyloxy)ethanol (P1, 175 mg; P2, 350 mg; and P3, 700 mg) along with α-pinene and ethanol for attracting
M. alternatus
. Treatments included (i) Ctrl, untreated control; (ii) H, α-pinene (3.78 g) and ethanol (1.26 g); (iii) H + P1; (iv) H + P2; and (v): H + P3. In each block, traps were randomly installed 50 m between traps, approximately 1.2 m high above the ground using poles. The pesticide Vapor-tape II (2,2-dichlorovinyl dimethyl phosphate) (Hercon Environmental) was placed in the trap to prevent escape of the captured beetles.
- Statistical analysis
The linear model for the experiment is
xij
= μ +
bi
+
tj
+
eij
, whereby μ is overall mean,
bi
is the effect of block (
i
= 1, 2, 3, and 4),
tj
is the effect of treatment (
j
= 1, 2, 3, 4, and 5), and
eij
is random error. The data collected were analyzed by two-way ANOVA. Data were transformed using the square root of (x + 0.5) before analysis for normality
[17]
.
Results and Discussion
A total of 27
M. alternatus
(10 males and 17 females) were captured from 20 traps which were allocated into four blocks of five treatments (
Fig. 2
). Blocks 1, 2, 3, and 4 had on average 0.75, 1.25, 3.0, and 1.75 beetles per trap, respectively. The block 1 located near the campus of a local college contained the least
M. alternatus
captured, whereas blocks 3 and 4 located close to a paddy field contained slightly more
M. alternatus
. There was no significant difference among the four blocks.
However, significant differences were detected among the five treatments (ANOVA: F=5.41; df=4, 12;
p
<0.01). On average, 0.5 beetles per trap were attracted to lure H containing α-pinene and ethanol, but the number was not significantly different from untreated control (
Fig. 3
). Lures H+P1 and H+P2 showed similar effectiveness with mean numbers of 1.75 and 1.0 beetles per trap, respectively, suggesting that the aggregation pheromone is more effective for attracting
M. alternatus
over α-pinene and ethanol (
Fig. 3
). Although lure P2 (350 mg) contained twice the amount of 2-(undecyloxy)ethanol per trap as compared with P1 (175 mg), less
M. alternatus
were captured in traps containing lure H+P2 than traps containing lure H+P1. These data suggest that a minimum 175 mg of 2-(undecyloxy)ethanol per trap could be used for recruitment of
M. alternatus
using cross-vane panel traps made of PET bottles. The highest number of
M. alternatus
(n=14, 52% of all beetles captured) was captured in traps with lure H+P3 containing 700 mg of 2-(undecyloxy)ethanol, 3.5 beetles per trap, versus any other treatments (
p
<0.01) (
Fig. 3
). In each treatment, both sexes of
M. alternatus
were attracted to lures containing α-pinene and ethanol (H) and/or 2-(undecyloxy)ethanol (P), but the numbers of males and females captured in each treatment were not significantly different. Our results are consistent with those of
Pajares et al. (2010)
, who reported that a high release rate of 41 mg of 2-(undecylxoy)ethanol per trap is more effective than a low release rate for attracting
M. galloprovincialis
. As the infected pine trees in the experiment site had been cut down and fumigated or crushed to small wood chips every year, not many
M. alternatus
were living there.
Two-week field bioassay results from June 24, 2014 to July 7, 2014. A total of 27 M. alternatus (10 males and 17 females) were captured. Ctrl, untreated control; H, α-pinene (3.78 g) and ethanol (1.26 g); P1, P2, and P3, 2-(undecyloxy)ethanol (175, 350, and 700 mg, respectively). Data represent mean ± S.E. of each treatment. White bars represent males and black bars represent females.
In conclusion, we demonstrated that a high dose of male-produced aggregation pheromone 2-(undecyloxy)ethanol (700 mg per trap) is effective for attracting
M. alternatus
at a previously pine wilt disease-affected site in Korea using cross-vane panel traps made of PET bottles and acrylic sheets. Our results suggest that the aggregation pheromone could be used for monitoring of pest control measures for pine wilt disease as well as detection and population monitoring of pine sawyer beetles. Further study is needed to elucidate the effect of 2-(undecyloxy)ethanol along with host plant volatiles on recruitment of
M. saltuarius
.
Acknowledgements
The authors thank Byeong-Yoon Seo and Woong Jang for the construction of traps and Dr. Kwang-Soo Choi for statistical analysis. This work was supported by a Daegu University Research Grant (to C.L.).
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