• 검색 결과가 없습니다.

Behavioral Monitoring System for Mud Shrimp Upogebia major and the Photoresponse to Illumination with Different Wavelength LEDs

N/A
N/A
Protected

Academic year: 2021

Share "Behavioral Monitoring System for Mud Shrimp Upogebia major and the Photoresponse to Illumination with Different Wavelength LEDs"

Copied!
8
0
0

로드 중.... (전체 텍스트 보기)

전체 글

(1)

한수지 50(4), 413-420, 2017

413

Copyright © 2017 The Korean Society of Fisheries and Aquatic Science pISSN:0374-8111, eISSN:2287-8815 Korean J Fish Aquat Sci 50(4),413-420,2017

Original Article

서 론

(Upogebia major) (de Haan, 1841)

동북아시아등지의 갯벌에서서식하는갑각류이다

(Kinoshita, 2002; Liu and Liu,

2012).

한국서남해의조간대에서주로발견되는쏙은대규모

이루어지는특유의생물교반

(bioturbation)

활동

(Rowden and Jones, 1993)

통하여갯벌퇴적물을교반하거나저서 물의군집에영향을주는갯벌생태학연구에중요한종의하나 이다

(Wynberg and Branch, 1994).

쏙의이상발생이갯벌생태 계에미치는영향

(Hong, 2013)

비롯한다양한관심에도불구 하고

,

자세한분류학적위치

,

외부형태국내의지리적분포

,

서식처의구조

,

생리생태외에생태계공학측면에서의쏙의 기능과생리적특성등에대하여제한된정보만이알려져있다

.

쏙의갑작스런서식밀도증가는생물교반활동에따른퇴적

변화로인해기존생물들의서식지를침범하여생태계교란 유발하며

,

주변의갯벌생태계에영향을미치는것으로 려져있다

(Hong, 2013).

국내서해안일부갯벌에서는쏙의 증식으로인하여바지락의서식처가피해를받아생산량이

1/10

수준으로급감했던사례가보고된있으며개체의

절을위한연구필요성이제기되었다

(Park et al., 2013).

국내외 퇴치관련연구사례로는쏙의신경접합부에있는

acetylcholin-

esterase

활동을저해시켜과잉활동근육호흡마비로

죽음에이르게하는

Carbaryl (1-naphthyl methylcarbamate)

이라는살충제를간조시에갯벌에뿌려쏙에의한양식장 피해를줄이려는시도를있다

(Estes, 1986).

미국에서의 이러한시도가군집감소에는효과적이었다고보고되기는 하였지만

(Buchanan et al., 1985; Armstrong et al., 1989),

저서성무척추동물에도영향을미치는단점을보임에따라

쏙(Upogebia major)의 광반응 분석시스템 구축과 발광다이오드 (Light-Emitting Diode) 파장별 행동분석

장준철 1,2 ·정종균 2 ·허윤성 2 ·송재희 3 ·김종명 1 *

1부경대학교 수산생물학과, 2부경대학교 LED-해양 융합기술 연구센터, 3국립수산과학원 갯벌연구센터

Behavioral Monitoring System for Mud Shrimp Upogebia major

and the Photoresponse to Illumination with Different Wavelength LEDs

Jun-Chul Jang

1,2

, Jong-Kyun Chung

2

, Youn-Seong Hur

2

, Jae-Hee Song

3

and Jong-Myoung Kim

1

*

1 Department of Fisheries Biology, Pukyong National University, Busan 48515, Korea

2 LED-Marine Convergence Technology R&D center, Pukyong National University, Busan 48547, Korea

3 Tidal Flat Research Center, National Institute of Fisheries Science, Gunsan 54014, Korea

The increase in the number of mud shrimps Upogebia major is a concern because of their negative effects on shellfish aquaculture, including Manila clam Venerupis philippinatum along the west coast of Korea. This study developed a behavioral analysis system for aquatic animals using a set of monochromatic light-emitting diode (LED) modules covering the visible light range at similar intervals. Movements of mud shrimp were monitored using a tracking sys- tem under illumination with infra-red light and an LED of 660 nm wavelength without provoking stimulation. The minimum light intensity needed to induce a photoresponse by the mud shrimp was 10 μmole/m 2 /s under the condi- tions tested. Of the six kinds of LED illuminations tested, the most sensitive response was obtained with illumination with the 505 nm LED, followed in order by LEDs with peak wavelengths of 525 nm≒465 nm > 405 nm≒590 nm >

660 nm. These findings should help to identify LED sources that efficiently induce movement of the mud shrimp and also for monitoring movement without stimulating.

Key words: Mud shrimp Upogebia major , LED (Light Emitting Diodes), Photo-response

This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial Licens (http://creativecommons.org/licenses/by-nc/3.0/) which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.

https://doi.org/10.5657/KFAS.2017.0413 Korean J Fish Aquat Sci 50(4) 413-420, August 2017 Received 29 June 2017; Revised 18 July 2017; Accepted 31 July 2017

*Corresponding author: Tel: +82. 51. 629. 5919 Fax: +82. 51.629.5908

E-mail address: [email protected]

(2)

장준철

정종균

허윤성

송재희

김종명

414

비특이적살충제의사용이금지되었다

(Lindsay, 1961).

이러한 방법들의단점을만회하고자쏙의천적을활용하거나전기 등을사용하는방안이나

(Dumbauld et al., 2008)

양식방법 변형을통한피해저감방안다양한대책들이제시되었

(DeFrancesco and Murray, 2010).

장비를이용한서식 벌의경운방법의경우서식처를교란하여쏙을밖으로노출 시켜갈매기등에의한포식등으로어느정도서식량을 수는있으나매년경운을실시해야하는애로사항이있다

.

,

쏙의서식밀도와지반의경도에따라경운자체가어려운 갯벌들이존재할뿐만아니라

,

퇴적환경의물리적교란은퇴적 물의구조를변형시켜갯벌에서식하는동물과수생식물에 각한손상을주며표층생물에도어느정도영향을미치는것으 보고된

(Herkül et al., 2011)

있어현장적용의어려움이 예상된다

.

따라서환경에무해한방식의생물의조절방법개발 통한근본적인원인해결책모색을위해서는쏙의생리적 각을이용한유인이나제어생리적특성에대한많은 보가필요할것이다

.

LED (Light Emitting Diodes)

친환경적인조명기구로써

,

에너지효율이높고

,

수명이장점을가지고있어실내외의 다양한분야에서기존조명을대체해가고있다

.

복합파장을 나타내는자연태양광원이나기존의인공광원과는달리

LED

특정파장영역만조사할있는차별적인특성을가지고

(Migaud et al., 2007; Shin and Kim, 2009).

최근에는

LED

어류기반수산업에이용하는융합연구가진행되어

,

관상어 양식어종에대한파장스트레스

,

호르몬등의생리학적 분석

(Shin et al., 2011)

연구외에

,

주로집어등포획어종의 반응관련연구를중심으로행동학적실험이진행되었다

(Jang et al., 2016).

전복등의패류에서도

LED

조명을이용한융합 연구도진행된있으나

(Gao et al., 2016),

갑각류관련융합 연구사례는미흡한실정이다

.

연구에서는서해안지역의 간대패류양식장환경에영향을미치는쏙의친환경적인행동

제어와생리반응에대한기초자료를제공하기위하여자극

행동분석시스템을구축하고

LED

파장별행동특성을분석

하여조사유도되는유인

/

제어행동변화파장별영향 확인하였다

.

재료 및 방법

실험 생물

실험에사용된쏙은충남보령시주교면송학리갯벌에

137

마리를직접 획득하였으며

,

평균크기는 두흉갑장이

28.4±5.1 mm,

전장이

95.3±10.7 mm

이었다

.

운반된쏙은 경대학교

LED-

해양융합기술연구센터

0.5 ton

규모의순환 여과조에냉각장치를이용하여

18℃

에서

3

일간순치실험을 진행하였다

.

파장별광반응은수조당

20

마리

,

행동분석은

5

리의쏙으로실험을수행하였다

.

LED 조명 설계 및 광학 측정

실험을위해제작한조명은가시광선영역에서

6

가지단일 파장영역을선정하였다

.

광반응실험용조명기구는

LUXPIA (Suwon, Korea)

사에서구입한

LRU1056 (Red, 660 nm), LAU 1056 (Amber, 590 nm), LGH1056 (Green, 525 nm), LCH1056 (Cyan, 505 nm), LBH1056 (Blue, 465 nm), LVH1056 (Violet, 405 nm) LED package

사용하여제작하였다

. LED

모듈은

10

직렬

12

병렬로 설계하였으며

,

효과적인 방출을 위하여

Metal PCB

사용하였다

.

완성된

LED

모듈의크기는

420(L)

×320(W) ×50(H) mm

이며

,

덮개는

10 mm

두께의강화유리를 사용하여제작하였으며

,

수중에만빛이조사될있도록수위 맞춰가림판을설치하였다

.

실험에사용된조명은제어기를부착하여동일한광량이조사 되도록조절하여실험을진행하였다

.

동일한광량조건을확보 하기위하여적분구

(Withlight Co., Korea)

사용하여광학

Dark

Adaptation area

(A) (A)

0.3m 0.33m

0.07m

0.57m

Camera

Violet (405 nm) Blue (465 nm) Cyan (505 nm) Green (525 nm) Amber (590 nm) Red (660 nm)

1μmole /m

2

/s

10 μmole /m

2

/s

50 μmole /m

2

/s

Behavior analysis, Dark (1min) → Light (1min)

(465 nm) Blue

(505 nm) Cyan

Green (525 nm)

Fig. 1. (A) Structure diagram of the Y-type cage aquarium constructed for photo-response analysis, and (B) schematic diagram of the experimental set up for behavior analysis.

(3)

갯벌 양식장 쏙의 광반응 분석

415

정을실시하였으며

,

최고최저로조정한조명의단계별광량 라디오미터를사용하여측정하였다

.

수중투과율에따른 분석은실험용수조에서파장별광원으로부터거리간격을 두고라디오미터를통하여측정하였다

.

파장별 광반응

파장별광반응분석시스템은서로의빛이간섭하지않는 건의

Y

형태의수조로제작하였다

. Y

모형의접점지역에

20

마리를두고

1

시간이상암순응시킨

10

동안

LED

점등

,

실험수조양끝으로이동행동을보이는개체를계수 하여분석하였다

.

쏙이인지하는최소광량을확인하기위하여

3

가지의광량

(1, 10, 50 μmole/m

2

/s)

6

가지파장

(405, 465, 505, 525, 590, 660 nm)

조건으로광반응실험을진행하였다

. 행동분석

LED

광원이쏙의초기행동에미치는분석실험은

6

가지

장의

LED

반응하는최소광량인

10 μmole/m

2

/s

15

실험하였다

.

실험에사용된쏙은

5

마리이며바닥면과

LED

빛을조사하는부분을제외하고는흰색시트지를붙여

,

분석하 고자하는생물과의명암대조를이용하여추적하였다

.

실험수 조를원형받침대가운데에두고

,

바닥에쏙이인지하지못하는 적외선램프

(R95 IR Red, Philips lighting, Netherlands)

래에사용하여물체를탐지할있도록하였으며

, LED

광원은

수조의좌측면에배치하여수중으로만투과될있도록진행 하였다

.

동물행동분석은

Ethovision XT10 (Noldus, Wagenin- gen, Netherlands)

사용하여실험을진행하였으며

, 1

시간 충분히암순응시킨상태에서의움직임과

LED

조사

1

간의움직임을

CCD

카메라를사용하여촬영하고소프트웨어

사용하여속도변화차이를분석하였다

.

행동분석녹화

,

체의겹침현상으로인한불완전추적의경우에는행동분석 이터에서제외하였다

.

광원이쏙의움직임에미치는효과를 세히분석하기위하여유사한결과를보이는

3

가지파장을선정 하여동일한방법으로

3

회씩

5

세트의반복실험을실시하였다

.

CCD

카메라를이용하여조명점등전후의

1

분간의행동을

영하였으며

,

동물행동분석장치를이용하여움직임추적과 트맵분석을진행하였다

.

통계처리

실험의 결과의 통계 처리는

SPSS

프로그램

(version 23.0;

SPSS Inc., USA)

사용하였으며

,

평균값을일원분산분석

, Tukey

사후검정을통해

P<0.05

수준에서항목간의유의 적인차이를검정하였다

.

결론 및 고찰

광반응 모니터링 분석 시스템 구축

적분구를사용하여측정한조명의광학적특성은

Table 1

Fig. 2

나타내었다

.

사용된

LED

조명의최대파장반치폭 각각

Red (660/17.88 nm), Amber (590/18.87 nm), Green (525/31.43 nm), Cyan (505/31.30 nm), Blue (465/21.94 nm), Violet (405/16.52 nm)

나타났다

.

빛은파장별로수심에따른투과력이다르므로수조위치 따른광량을분석하기위하여

,

실험수조의끝에

LED

조명을두고수중거리별로투과되는광량을측정하였다

.

수중 에서

10

반복측정한광량을바탕으로작성한감소곡선을

(Fig.

3)

보면

, Y-

수조의끝에서조사한파장별광원은생물 위치한

0.5 m

지점에서는광량이각각

Violet (6.97%), Blue (9.39%), Cyan (9.02%), Green (8.56%), Amber (5.92%), Red

Table 1. Specification of LED modules constructed for monitoring the photo-response

Peak wavelength (nm) Full width at half maximum (nm) Radiant flux (mW) Current (A)

Violet 405 16.52 829.6 0.108

Blue 465 21.94 1438.6 0.104

Cyan 505 31.30 892.5 0.104

Green 525 31.43 1417.5 0.105

Amber 590 18.87 486.2 0.099

Red 660 17.88 1106.5 0.096

LED illumination

1 μmole 10 μmole 50 μmole

Relative sensitivity (%)

0 10 20 30 40 50

b

a a

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 10 30 40

50 bc bc c bc

ab a

abc

150 200

ab bc

c bc

a ab Distance (m)

Penetration ratio (%)

0.0 100

80 60 40 20 0

Violet Blue Cyan Green Amber Red

0.2 0.4 0.6 0.8 1.0

Wavelength (nm)

Light intensity [mW]

60 50 40 30 20 10 0

400 450 500 550 600 650 700

Violet

Amber Red Green

Cyan Blue

Fig. 2. Spectral power distributions of LED sources measured by using an integrating sphere.

(4)

장준철

정종균

허윤성

송재희

김종명

416

(4.64%)

였으며

, 1 m

떨어진지점에서의광량은각각

Violet (5.59%), Blue (7.28%), Cyan (6.30%), Green (5.92%), Amber (5.47%), Red (4.23%)

으로나타났다

.

결과는빛의진행방향 대하여수직방향의조도가거리의제곱에반비례한다는 전의연구결과

(Choi, 2006; Choi et al., 2010)

유사하게 원으로부터멀어질수록광량이급격하게낮아짐을 보여준다

.

실험수조에서광원이위치한것과반대방향수중환경의

광량은대부분파장에서광량에비해

90%

이상감소하였으

, 660 nm

LED

조명에서가장손실이있음을있었

.

또한

-

녹계열파장의투과율이적색광보다높게나타났는

,

이는수중미립자밀도로인한장파장의흡수로판단된다

.

광반응분석수조는조명의광량쏙의움직임등을고려하

,

서로의빛이간섭하지않는조건의

Y

형태수조로제작하 였다

.

이를위하여

0.57(L)×0.33(W)× 0.3(H) m

사각형

3

개를연결하여

Y

형태로만들었으며

,

수조끝에는 부에조명을넣을있도록

0.07 m

간격을두어제작하 였다

.

행동분석수조는

0.5(L)×0.3(W)×0.3(H) m

크기의 각수조에서진행되었으며

Fig. 4

나타내었다

.

광량/파장별 광반응

파장에따른광반응은수온

18℃

암실수조에서순치한

6

가지파장의

LED

광원자극을다음

10

초간의이동 동을분석하였으며

,

대조구로빛이없는암실조건

(Dark)

용하였다

.

쏙의움직임을유도하는데필요한최소광량을알아 보기위하여

LED

광원별로

1 μmole/m

2

/s

에서

l0 μmole/m

2

/s,

그리고

50 μmole/m

2

/s

광량을증가시키면서쏙의움직임의 차이를분석하였다

(Fig. 5).

광량실험결과를종합해보면

6

파장전체에서광량

1 μmole/m

2

/s

에서는암조건에서의움직임 다른차이가발견되지않았으나

,

광량이

l0 μmole/m

2

/s

증가하는경우에는광반응이

34%

에서

40.9%

증가하였으며

, 50 μmole/m

2

/s

증가할경우에는

41.4%

10 μmole/m

2

/s

통계학적으로유사한경향을나타내었다

.

앞선결과를바탕으

l0 μmole/m

2

/s

이상의광량이광반응을유도할있는광량 으로나타났으며

,

파장별광반응실험은

l0 μmole/m

2

/s

광량을 기준으로실험을진행하였다

.

파장별광반응분석결과를보면

405 nm-525 nm

가시광선영역 에서는

Violet (43.0 %), Blue (43.0%), Cyan (43.5%), Green (43.0%)

파장이

43%

이상의광반응을나타내는것으로나타났으

,

이외의파장에서는

Amber (40.5%)

그리고

Red (37.0%)

Dark (36.5%)

유의적인 차이를 나타내었다

.

통계분석

, Dark

상태를기준으로

Violet (P=0.017), Blue (P=0.034), Cyan (P=0.017), Green (P=0.034) Amber (P=0.449), Red (P=1.000)

나타났다

.

결과는

amber

red

같은장파장

LED illumination

1 μmole 10 μmole 50 μmole

Relative sensitivity (%)

0 10 20 30 40 50

b

a a

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 10 30 40

50 bc bc c bc

ab a

abc

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 100 150 200

ab bc

c bc

a a

ab Distance (m)

Penetration ratio (%)

0.0 100

80 60 40 20 0

Violet Blue Cyan Green Amber Red

0.2 0.4 0.6 0.8 1.0

Wavelength (nm)

Light intensity [mW]

60 50 40 30 20 10 0

400 450 500 550 600 650 700

Violet

Amber Red Green

Cyan Blue

Fig. 3. Underwater penetration characteristics of LEDs measured from the surface of the experimental tank.

Dark

Adaptation area

(A) (A)

0.3m 0.33m

0.07m

0.57m

Camera

Violet (405 nm) Blue (465 nm) Cyan (505 nm) Green (525 nm) Amber (590 nm) Red (660 nm)

1μmole /m

2

/s

10 μmole /m

2

/s

50 μmole /m

2

/s

Behavior analysis, Dark (1min) → Light (1min)

(465 nm) Blue

(505 nm) Cyan

Green (525 nm)

Fig. 4. Experimental tanks illuminated with LEDs of different wavelengths (dark, no light; violet 405nm; blue 465 nm; cyan 505 nm;

green 525 nm; amber 590 nm and red 660 nm) and light intensities of 1, 10, and 50 µmole/m2/s.

(5)

갯벌 양식장 쏙의 광반응 분석

417

계열

(< 590 nm)

에서는빛에따른반응이낮았음을확인할 있었으며

, 650 nm

Red

광원은암실에서와마찬가지로빛의 자극을유도하지않아

IR

대신에관찰용조명등으로이용하기 적합한것으로판단된다

(Fig. 6).

행동분석

파장별광반응유도효과를기반으로세부행동분석을위하여

,

파장별자극쏙의

1

분간움직임을

CCD

카메라를사용하여 녹화하여분석하였다

.

앞선실험과마찬가지로

6

가지파장 사용하였으며

, 1

시간이상암순응시킨

,

암순응상태와

점등시의이동속도차이를분석하여

Fig. 7

나타내었다

.

3

회씩

5

세트의반복실험한결과암순응에서평균속도는

1.117±0.15 cm/s

이며

, 1

시간이상암순응

LED

조명을점등 상태에서의평균속도는각각

1.379±0.87 cm/s (405 nm), 1.656±0.89 cm/s (465 nm), 2.183±1.76 cm/s (505 nm), 1.743±1.32 cm/s (525 nm), 1.615±1.15 cm/s (590 nm), 0.904±0.84 cm/s (660 nm)

나타났다

.

파장

LED

속도변화율분석은암순응상태의평균속도를

100%

기준으로 설정하고 실험마다 속도 증가율의 평균을 합하여계산하였다

.

속도증가율의 평균은

140.0±30.4%

(405 nm), 172.2±31.4% (465 nm), 193.0±32.0% (505 nm), 175.2±25.9% (525 nm), 143.0±28.4% (590 nm), 102.6±

22.6% (660 nm)

나타났으며결과를토대로분석한파장 움직임은

505 nm>525 nm≒465 nm>590 nm≒405 nm>>

660 nm≒Dark

순서로나타났다

.

통계분석결과는

Dark

상태 기준으로

Violet (P=0.098), Blue (P=0.008), Cyan (P=0.000), Green (P=0.000), Amber (P=0.061), Red (P=1.000)

나타났 으며이는

-

계열

(465-525 nm)

에서의유의적인차이를 인할있었다

.

이러한결과를바탕으로파장별광반응효과를

자세히분석하기위하여

,

가장민감한반응을나타낸

-

열의

3

가지파장

(465, 505, 525 nm)

대상으로동일한방법 으로추가실험을진행하였으며광원에따른쏙의움직임을 트맵과트래킹을이용하여분석하였다

(Fig. 8).

연구결과 평균이동거리를보면암순응상태에서는

79.80±11.06 cm

,

조명점등

105.44±53.58 cm (465 nm), 149.75±63.79 cm (505 nm), 123.32±61.60 cm (525 nm)

각각나타났다

.

암순응평균이동거리를

100%

기준으로설정하여환산할 경우

, 148.3±38.5% (465 nm), 169.7±25.9% (505 nm), 160.2±17.6% (525 nm)

나타났다

.

파장별이동거리 증가 평균은

505 nm>525 nm≒465 nm >> Dark

나타났으

,

암순응상태기준통계분석결과는

Blue (P=0.013), Cyan

Fig. 5. Photosensitivity analysis of mud shrimp Upogebia major

measured upon three (1, 10, and 50 μmole/m2/s) intensities of LED illumination. a-b Means with superscripts bars are significantly dif- ferent (P < 0.05).

LED illumination

1 μmole 10 μmole 50 μmole

Relative sensitivity (%)

0 10 20 30 40 50

b

a a

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 10 30 40

50 bc bc c bc

ab a

abc

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 100 150 200

ab bc

c bc

a a

ab Distance (m)

Penetration ratio (%)

0.0 100

80 60 40 20 0

Violet Blue Cyan Green Amber Red

0.2 0.4 0.6 0.8 1.0

Wavelength (nm)

Light intensity [mW]

60 50 40 30 20 10 0

400 450 500 550 600 650 700

Violet

Amber Red Green

Cyan Blue

Fig. 6. Photoresponse analysis of mud shrimp Upogebia major with different LED wavelengths. a-c Means with superscripts bars are significantly different (P<0.05).

LED illumination

1 μmole 10 μmole 50 μmole

Relative sensitivity (%)

0 10 20 30 40 50

b

a a

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 10 30 40

50 bc bc c bc

ab a

abc

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 100 150 200

ab bc

c bc

a a

ab Distance (m)

Penetration ratio (%)

0.0 100

80 60 40 20 0

Violet Blue Cyan Green Amber Red

0.2 0.4 0.6 0.8 1.0

Wavelength (nm)

Light intensity [mW]

60 50 40 30 20 10 0

400 450 500 550 600 650 700

Violet

Amber Red Green

Cyan Blue

Fig. 7. Relative sensitivity (%) of mud shrimp Upogebia major reflected in the change of speeds upon illumination of LEDs as compared to that of the movement in the dark (100%). a-c Means with superscripts bars are significantly different (P<0.05).

LED illumination

1 μmole 10 μmole 50 μmole

Relative sensitivity (%)

0 10 20 30 40 50

b

a a

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 10 30 40

50 bc bc c bc

ab a

abc

LED illumination

Violet Blue Cyan Green Amber Red Dark

Relative sensitivity (%)

0 100 150 200

ab bc

c bc

a a

ab Distance (m)

Penetration ratio (%)

0.0 100

80 60 40 20 0

Violet Blue Cyan Green Amber Red

0.2 0.4 0.6 0.8 1.0

Wavelength (nm)

Light intensity [mW]

60 50 40 30 20 10 0

400 450 500 550 600 650 700

Violet

Amber Red Green

Cyan

Blue

(6)

장준철

정종균

허윤성

송재희

김종명

418

(P=0.001), Green (P=0.002)

나타났다

.

히트맵분석에서는

1

분간빛에노출된쏙이머무르는지역을나타내었으며조명이 점등된후에는점등전보다쏙이수조내부에서지속적인움직 임이있었음을확인할있었다

.

연구에서는갯벌양식장의침탈생물의하나인쏙을대상

으로

LED

파장에따른행동분석시스템을구축하고

LED

파장

자극에따른움직임의차이를확인하였다

. LED

파장별

반응결과는특정한영역

(405-590 nm)

가시광선을인지하는

것으로판단되며

, 660 nm

이상의장파장영역은인식하지못하

것으로판단된다

.

가시광선영역에서도특히

-

계열의 파장영역에서반응을나타내었으며

,

-

계열의

3

가지 파장중에서도

505 nm

에서평균속도가

169.7%

증가하는것으 Fig. 8. Behavior analysis (heat-map, tracking) of mud shrimp Upogebia major upon illumination of Blue (465 nm), Cyan (505 nm), and Green (525 nm) LEDs. In contrast to the movement observed in the dark, the right side showed the tracking of the movement observed upon illumination of LEDS of different wavelengths as indicated.

Dark

Adaptation area

(A) (A)

0.3m

0.33m

0.07m

0.57m

Camera

Violet (405 nm) Blue (465 nm) Cyan (505 nm) Green (525 nm) Amber (590 nm) Red (660 nm)

1μmole /m

2

/s

10 μmole /m

2

/s

50 μmole /m

2

/s

Behavior analysis, Dark (1min) → Light (1min)

(465 nm) Blue

(505 nm) Cyan

Green

(525 nm)

(7)

갯벌 양식장 쏙의 광반응 분석

419

나타났으며

, 465 nm

525nm

각각

148.3%, 160.2%

결과를나타내었다

.

이와마찬가지로히트맵분석결과도

LED

점등

505 nm

에서가장활발한행동변화를나타내며

,

쏙의 광반응이동거리변화에서

169.7%

505 nm

에서가장 나타났다

.

어류의광반응연구로는대표적인집어등포획어종인고등어

,

오징어의파장별광반응실험에서도마찬가지로해당생물의 시각수용체최대흡광파장영역인

500 nm

영역근처에서가장 반응성을나타내었다

.

또한

, LED

이용한갈치의행동분 석에서는청색광에대한반응이가장뛰어난것으로나타났다

(Kim et al., 2016).

동안진행되어시각관련연구의경우 에는대부분어류에해당하는연구가대부분이었으며

,

갑각류 경우는현미분광측정법

(microspectrophotometry)

전기생 리학적

(electrophysiology)

방법을통해연구가진행되었다

.

고된연구내용으로는

Mantis shrimps (Crustacea; Stomatop- oda; Gonodactylidae)

광세포특성에대한연구가있으며

,

재까지알려진구각목에서의망막주변시각색소의최대흡광 분포가평균

504.4±12 nm

나타났으며

(Cronin et al., 1994a;

Cronin et al., 1994b), Orconectes virilis, Callinectes sapidus, Panulirus argus

시각민감도분석결과

,

각각

565 nm, 507

nm, 510 nm

에서간상세포의최대흡광도를나타내는것을

있었다

(Goldsmith and Fernandez, 1968; Cummins and Goldsmith, 1981; Cummins et al., 1984).

이러한갑각류의 각분석간상세포의최대흡광도결과로

,

실험에서의

500 nm

근방에서반응을최대로유도하는결과와유사하게

타났으며이는수중투과정도와간상세포의최대흡광파장 영역과의연관성이있을것으로판단된다

.

따라서

,

이에따른 시각분석에관련된추가적인연구가필요하다고판단된다

.

결론적으로쏙은평균적으로

505 nm

영역에서다른파장보 민감한반응을나타내는것을있었으며

,

이는쏙의 시각과관련된시각세포와광반응과의상관관계분석이필요 것으로판단된다

.

쏙이인식하지못하는

Red LED

쏙의 동을유발하지는않으므로쏙의야간행동을관찰하는데적절 광환경을제시하는것으로판단된다

.

따라서추가적인쏙의 시각분석을통하여광반응을유도하는최적의파장조건을 립하면

,

쏙의친환경적인구제에중요한연구자료가것이다

사 사

연구는부경대학교자율창의학술연구비

(2016)

년에의해 수행되었습니다

.

References

Armstrong DA, Dumbauld B and Doty D. 1989. Oyster culture and crab habitat: conflicts over use of the insecticide Sevin in coastal estuaries. Northwest Environ J 5, 185-187.

Buchanan DV, Bottom DL and Armstrong DA. 1985. The con- troversial use of the insecticide Sevin in Pacific Northwest estuaries: its effects on dungeness crab, Pacific oyster, and other species. In: Proceedings of the symposium on Dunge- ness Crab biology and management. Alaska Sea Grant Re- port. Anonymous, 401-417.

Choi SK, Kim SJ, Park DW, Kil GS, Choi CY and Song SB.

2010. Design and fabrication of an energy saving LED-fish- ing lamp. J Korean Soc Mar Eng 34, 515-521. https://doi.

org/10.5916/jkosme. 2010.34.4.515.

Choi SJ. 2006. Radiation and underwater transmission charac- teristics of a high-luminance Light-emitting Diode as the light source for fishing lamp. J Kor Fish Soc 39, 480-486.

https://doi.org/10.5657/kfas.2006.39.6.480.

Cronin TW and Marshall NJ. 1989. A retina with at least ten spectral types of photoreceptors in a mantis shrimp. Nature 339, 137-140. https://doi.org/10.1038/339137a0.

Cronin TW, Marshall NJ, Quinn CA and King CA. 1994a. Ul- traviolet photoreception in mantis shrimp. Vision Res 34, 1443-1452. https://doi.org/10.1016/0042-6989(94)90145-7.

Cronin TW, Marshall NJ and Caldwell RL. 1994b. The retinas of mantis shrimps from low-light environments (Crustacea;

Stomatopoda; Gonodactylidae). J Comp Physiol A 174, 607- 619. https://doi.org/10.1007/bf00217382.

Cummins D, Chen D and Goldsmith TH.1984. Spectral sensi- tivity of the spiny lobster Panulirus argus. Biol Bull 166, 269-276. https://doi.org/10.2307/1541448.

Cummins D and Goldsmith TH. 1981. Cellular identification of the violet receptor in the crayfish eye. J Comp Physiol 142, 199-202. https://doi.org/10.1007/bf00605738.

DeFrancesco J and Murray K. 2010. Pest Management Strategic Plan for Bivalves in Oregon and Washington. In: Summary of a workshop. Oregon State University, Washington D.C., U.S.A., 3-88.

Dumbauld BR, Holden DL and Langness OP. 2008. Do stur- geon limit burrowing shrimp populations in Pacific North- west Estuaries? Env Biol Fish 83, 283-296. https://doi.

org/10.1007/s10641-008-9333-y.

Estes PS. 1986. Cardiovascular and respiratory responses of the ghost shrimp, Callianassa californiensis Dana, to the pesti- cide carbaryl and its hydrolytic product 1-naphthol. Thesis, Oregon State University, Washington D.C., U.S.A.

Gao X, Zhang M, Li X, Song C and Liu Y. 2016. Effects of light quality and intensity on the growth, survival and metamor- phosis of Haliotis discus hannai Ino larvae. Aquaculture Res 48, 3369-82. https://doi.org/10.1111/are.13164.

Goldsmith TH and Fernandez HR. 1968. Comparative studies of crustacean spectral sensitivity. J Comp Physiol 60, 156- 175. https://doi.org/10.1007/bf00878449.

Herkül K, Kotta J and Paernoja M. 2011. Effect of physical dis- turbance on the soft sediment benthic macrophyte and inver- tebrate community in the northern Baltic Sea. Boreal Env

(8)

장준철

정종균

허윤성

송재희

김종명

420

Res 16, 209-219.

Hong JS. 2013. Biology of the mud shrimp Upogebia major (de Haan, 1841), with particular reference to pest manage- ment for shrimp control in manila clam bed in the west coast of Korea. Ocean Polar Res 35, 323-349. https://doi.

org/10.4217/opr.2013.35.4.323.

Jang JC, Choi MJ, Yang YS, Lee HB, Yu YM and Kim JM.

2016. Dim-light photoreceptor of chub mackerel Scomber japonicus and the photoresponse upon illumination with LEDs of different wavelengths. Fish Physiol Biochem 42, 1015-1025. https://doi.org/10.1007/s10695-015-0193-z.

Kim MK, An YL, Park SH, Oh TC, Kang HC and Park YS.

2016. Behavioral reaction of hairtail (Trichinus lepturus) to different colors of LED light. J Korean Soc Fish Technol 52, 183-190. https://doi.org/10.3796/ksft.2016.52.3.183.

Kinoshita K. 2002. Burrow structure of the mud shrimp Upogebia major (Decapoda: Thalassinidea: Upogebiidae). J Crust Biol 22, 474-480. https://doi.org/10.1163/20021975-99990255.

Lindsay C. 1961. Pesticide tests in the marine environment in the State of Washington. In: Proc Nat Shellfisheries Assoc 52, 87-97.

Liu W and Liu R. 2012. A new species of the genus Austinogebia Ngoc-Ho, 2001 (Crustacea, Decapoda, Gebiidea, Upogebi- idae) from northern China. Zootaxa 3243, 59-64. https://doi.

org/10.1163/15685403-00003444.

Migaud H, Cowan M, Taylor J and Ferguson HW. 2007. The effect of spectral composition and light intensity on mela- tonin, stress and retinal damage in post-smolt Atlantic salmon, Salmo salar. Aquaculture 270, 390-404. https://doi.

org/10.1016/j.aquaculture.2007.04.064.

Park KW, Song JH, Choi YS and An KH. 2013. Changes in den- sity and culture conditions of the Manila Clam Ruditapes philippinarum on the West coast of Korea. Korean J Malacol 29, 207-216. https://doi.org/10.9710/kjm.2013.29.3.207.

Rowden AA and Jones MB. 1993. Critical evaluation of sediment turnover estimates for Callianassidae (Decapoda: Thalas- sinidea). J Exp Mar Biol Ecol 173, 265-272. https://doi.

org/10.1016/0022-0981(93)90057-u.

Shin HS, Lee J and Choi CY. 2011. Effects of LED light spec- tra on oxidative stress and the protective role of melatonin in relation to the daily rhythm of the yellowtail clownfish,

Amphiprion clarkii. Comp Biochem Physiol A: Mol Integrat

Physiol 160, 221-228. https://doi.org/10.1016/j.cbpa.2011.

06.002.

Shin M and Kim J. 2009. Introduction to LED packaging tech- nology. Books-hill, Seoul, Korea.

Wynberg RP and Branch GM. 1994. Disturbance associated with bait-collection for sandprawns (Callianassa kraussi) and mudprawns (Upogebia africana): long-term effects on the biota of intertidal sandflats. J Mar Res 52, 523-558.

https://doi.org/10.1357/0022240943077019.

수치

Fig. 1.  (A) Structure diagram of the Y-type cage aquarium constructed for photo-response analysis, and (B) schematic diagram of the  experimental set up for behavior analysis.
Fig. 2. Spectral power distributions of LED sources measured by  using an integrating sphere.
Fig. 4. Experimental tanks illuminated with LEDs of different wavelengths (dark, no light; violet 405nm; blue 465 nm; cyan 505 nm;
Fig. 6. Photoresponse analysis of mud shrimp Upogebia  major  with different LED wavelengths

참조

관련 문서

Milk, buckwheat, peanut, soybean, wheat, mackerel, crab, shrimp, pork, peach,. tomato, walnut, chicken,

In the current context, where the interconnectedness of the global economy has intensified greatly and the importance of a collective response to

Identification of a missense mutation in the bovine ABCG2 gene with a major effect on the QTL on chromosome 6 affecting milk yield and composition in Holstein cattle.. Evidence

Taken together, the results of correlation analysis exhibit four major findings: (1) DK rates for behavioral items have only a weak, or moderate at best, correlation with

The index is calculated with the latest 5-year auction data of 400 selected Classic, Modern, and Contemporary Chinese painting artists from major auction houses..

The “Asset Allocation” portfolio assumes the following weights: 25% in the S&amp;P 500, 10% in the Russell 2000, 15% in the MSCI EAFE, 5% in the MSCI EME, 25% in the

1 John Owen, Justification by Faith Alone, in The Works of John Owen, ed. John Bolt, trans. Scott Clark, &#34;Do This and Live: Christ's Active Obedience as the

In this thesis, we studied the enhancement of the light extraction efficiency in InGaN-based light-emitting diodes (LEDs) patterned with nano structures.. The