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Transcript of Chuanxin Qin Ph. D South China Sea Fisheries Research Institute, CAFS Gerard DiNardo Ph.D Pacific...
Stock Assessment Methodologies of reef systems: A Case study
Using Yangmeikeng Artificial Reef
Chuanxin Qin Ph. D South China Sea Fisheries Research Institute, CAFSGerard DiNardo Ph.D Pacific Islands Fisheries Science center, NOAAPimao Chen Prof. South China Sea Fisheries Research Institute, CAFS
Hui-Hua Lee Ph.D Pacific Islands Fisheries Science center, NOAA
Contents
2 Results
3 Conclusion
4 Next step plan
Exchange contents1
Exchange contents
1
What did we do in Hawaii?
Contents: what did we do in Hawaii…
The content, method, data require, and data processing software of artificial reef fisheries resource stock assessment.
Introduced to R software for use in stock assessment The fishery resources and resource management status in
Hawaii and South China Sea were discussed. China’s Summer Fishing Moratorium (close season), stocking enhancement, artificial reef construction, MPA and other management strategies for fishery resources recession in China were discussed too.
Some similarities between artificial reef stock assessment and coral reef stock assessments. Thus, the statistics methods used in coral reef stock assessment can apply to artificial reef.
Results
2
What did we get?
1Fisheries and Management in the Guangdong Province, China: Challenges and Recent Developments
2Evaluating the Efficacy of Artificial Reefs in the Guangdong Province, China: A Case study Using Yangmeikeng Artificial Reef
1Fisheries and Management in the Guangdong Province, China: Challenges and Recent Developments
Rich biodiversity, high valuation
Rich biodiversity: fish species – 229, shellfish species – 84 , cephalopodium species – 17, ( Jia et al. , 2012 )
Fishery Production Ecnomic valuation
1% 2%
9%3%
6%
18%
15%
19%
20%
4% 3%
天津 河北
辽宁 上海
江苏 浙江
附件 山东
广东 广西
海南
0%2%
10%1%
5%
23%
14%
21%
13%
6%4%
0% 2%
8%0%
5%
23%
16%
20%
12%
6% 8%
1990
2000
2010
The figure showed the China’s fishery economic valuation from 1990 to 2010
Guangdong
1992
1993
1994
1996
2000
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
0
20
40
60
80
100
120
140
160
年份 , Year
产值,亿元
Fishery economic valuation of Guangdong province from 1992 to 2011
Ten billions
Commercial fisheries Commercial Fisheries – trawl, gillnet, trap,
landline Fishery species – fish, shrimp, crab, shellfish…
50’ - 70’
80’ – to now
Challenge Environmental pollution
Challenge Fishery resource decrease Sea-related projects Red tide
1980s 起
Year CPUE (kg/h) Catch (104 tons / Year) High value Trash fish 1970s: 207.26 150 90% 5% 2000s: 30.62 340 15% 80%
以南海为例(潜在渔获量 224~260 万吨):
近海渔业资源质量下降 产卵场栖息地生态恶化
捕捞过度 环境污染 作业破坏
营养级下降
Total catch in Guangdong Province
1950
1953
1956
1959
1962
1965
1968
1971
1974
1977
1980
1983
1986
1989
1992
1995
1998
2001
2004
2007
2010-300000
200000
700000
1200000
1700000
2200000Other species
Macroalgae
Shellfish
Shrimp&Crab
Fish
Year
Catc
h,
tons
The catches of fishery resource in Guangdong province China
Data collection - Fisheries Statistical Yearbook Data – catch from 1950 to 2010
CPUE
1986
1987
1988
1989
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
0
50
100
150
200
250
300others Line@angle stow net Gill net
Pursue Trawl
Year
CP
UE,
Tons p
er
vessel
The fluctuation of CPUE of different fishing methods
Vessel
1953
1956
1959
1962
1965
1968
1971
1974
1977
1980
1983
1986
1989
1992
1995
1998
2001
2004
2007
2010
0
20000
40000
60000
80000
Unmotorized vessel
Motor vessel
Year
Fis
h V
essel
Conclusion From 1950 to 1980 catch of fishery in Guangdong
Province was growth slowly. The catch have changed dramatically since
1980’s. The steeply increasing was shown from 1981 to
1998. The total catch has more than four times since 1980 to 1954500 Tons in 1998.
Since then, the obvious decrease was shown. In recent years catch increased slightly
Fisheries management strategies in Guangdong province:
China’s Summer Fishing Moratorium (Close Season)
Object – Protect the fishery resource, sustainability… Initial - 1999
Fisheries management strategies in Guangdong province:
Stocking enhancement Object: restoration of fishery resource Initial: 1980, large scale from 2001 Species : fish, shrimp, shellfish, sea turtle,
macroalgae… Up to dozens of varieties…
Fish
•Lutianus argentimaculatus, Lutjanus sanguineus, Acanthopagrus schlegel, parus latus, Plectorinchus cinctus
shellfish
•Chlamys nobilis, Meretrix meretrix, Paphia undulata, Mactra antiquata
Macroalge
•Porphyra sp., Gracilaria sp., Laminaria japonica, Sargassum sp.
Shrimp
•Penaeus monodon, Penaeus japonicus, Fenneropenaeus chinensis, Penaeus ( Fenneropenaeus) Penicillatus, Penaeus merguiensis
Why we selected these species
Local species
Economic evaluation
Food web: feed…
SeedBiodiversity
When we stocking…During stocking the fishery is closed Time: China’s Summer Fishing Moratorium in
2008 Why: prevent the larval from fishermen Release fishing festival: Promot, Spur
No. Species Quantity, million per year1 花鲈 Lateolabrax japonicus 4 2 青石斑鱼 Epinephelus awoara 2 3 斜带石斑鱼 Epinephelus coioides 14 卵形鲳鲹 Trachinotus ovatus 25 军曹鱼 Rachycentron canadum 0.56 大黄鱼 Pseudosciaena crocea 2 7 紫红笛鲷 Lutianus argentimaculatus 28 红笛鲷 Lutjanus sanguineus 29 星斑裸颊鲷 Lethrinus nebulosus 210 真鲷 Pagrus major 311 平鲷 Rhabdosargus sarba 412 黑鲷 Acanthopagrus schlegel 413 黄鳍鲷 Sparus latus 314 断班石鲈 Pomadasys hasta 215 三线矶鲈 Parapristipoma trilineatus 416 花尾胡椒鲷 Plectorinchus cinctus 1.8 17 斑节对虾 Penaeus monodon 50 18 日本对虾 Penaeus japonicus 50 19 中国对虾 Fenneropenaeus chinensis 20 20 长毛对虾 Penaeus ( Fenneropenaeus ) Penicillatus 100 21 墨吉对虾 Penaeus merguiensis 100 22 杂色鲍 Haliotis diversicolor 0.5 23 华贵栉孔扇贝 Chlamys nobilis 300 24 文蛤 Meretrix meretrix 400 25 波纹巴非蛤 Paphia undulata 300 26 西施舌 Mactra antiquata 20 27 绿海龟 Chelonia mydas 0.0028 28 中国鲎 Tachpleus tridentatus 4 29 大珠母贝 Pinctada maxima 1.6 30 紫菜 Porphyra sp. 431 宽额鲈 Promicrops lanceolatus 0.232 黄唇鱼 Bahaba flavolabiata 0.233 海萝 Gloiopeltis sp. 234 蜈蚣藻类 Grateloupia sp. 135 江蓠类 Gracilaria sp. 436 麒麟菜类 Eucheumae sp. 237 海带 Laminaria japonica 1.538 马尾藻类 Sargassum sp. 639 蕨藻类 Caulerpa sp. 2
the plan of stocking enhancement in Guangdong province from 2010 to 2015 (Chen et al., 2009)
Fisheries management strategies in Guangdong province:
Artificial reef construction History: Rich experiences of artificial reef
achieved in Guangdong during 1981-1985, large scale construction from 2001 - Plan of artificial reef deployment
Construction schedule and scale
2000 2002 2004 2006 2008 2010 20120
50
100
150
200
250
0
20
40
60
80
100
120
140
160
180
200
Reef area
Construction area
Year
Re
ef
vo
lum
e,
10
5 m
3
Co
nstr
ucti
on
are
a,
km
2
Fisheries management strategies in Guangdong province:
Other management strategies
MPA – 1983-1990 (5), 1990 – 1998 (3), 1999 – 2003 (24)…
Fishing license Limit fishing (catch limit) Minimum legal size Gear constraint (mesh size) Buy-back (vessel) and substities (not to fish) Marine ranching combined with habitat
enhancement
1949 1959 1969 1979 1989 1999 20090.00E+00
5.00E+05
1.00E+06
1.50E+06
2.00E+06
2.50E+06
Year
Catc
h,
tons
Close season
Stocking enhancement
Artificial reef
The catch of Guangdong province from 1950 to 2010
Discussion: it works or not…
1985
1987
1989
1991
1993
1995
1997
1999
2001
2003
2005
2007
2009
0
5000
10000
15000
20000
25000
30000
Year
Garo
uper,
Tons
Catch of grouper from 1982 to 2010
1985
1987
1989
1991
1993
1995
1997
1999
2001
2003
2005
2007
2009
0
5000
10000
15000
20000
25000
30000
35000
40000
45000
50000
Year
larg
e y
ellow
cro
aker,
Tons
Catch of large yellow croaker from 1982 to 2010
1978
1980
1982
1984
1986
1988
1990
1992
1994
1996
1998
2000
2002
2004
2006
2008
2010
0
5000
10000
15000
20000
25000
30000
35000
40000
45000
50000
Year
Shri
mp,
Tons
Catch of shrimp
Guangdong’s coastal fishery
was overfishing
Fisheries management strategies in Guangdong province is
working now…
• Fishery resource increasing
• Environmental • Water quality• Others
Which one is best ?
• Stocking enhancement
• Close season• Artificial reef
construction• Others
How and when?
We expected…
2Evaluating the Efficacy of Artificial Reefs in the Guangdong Province, China: A Case study Using Yangmeikeng Artificial Reef
Survey Station design: how to select the station
Reef unit
Difference of reef structure
reef modules
Reef set
The same reef unit or difference reef unit, a large scale
Reef group
Many reef sets, different reef unite and reef set
Reef complexAssembling more than one group into coherent layout
The influence of water current
Water nutrition and fish…
Yangmeikeng Artificial reef
Construction time: Mar 20, 2007 to Dec 25, 2007 Reef Area: 2.65 km2
Construction scale: 12 type reef; 2272 reef, 18 reef group;
Reef volume: 95 100 m3
01号鱼礁
02号鱼礁
03号鱼礁
04号鱼礁
05号鱼礁
06号鱼礁
07号鱼礁
08号鱼礁
09号鱼礁
10号鱼礁
11号鱼礁
12号鱼礁
Reef modulesin Yangmeikeng reef
Reef groupin Yangmeikeng reef
Reef group 1
Reef group 2
Reef group 3
Reef complexin Yangmeikeng reef
Survey station in Yangmeikeng reef
Data source: which style data we need
Survey data: trawl, gill net… Historical data: trawl, gill net Survey time: Mar 2007 (control survey); Mar,
May, Aug, Nov 2008 and May 2009
Trawl data preliminary results
167 species fishery resoruce: 74 fish, 30 crab, 4 shrimp, 8 cephalopod, 35 scallop.
0
5
10
15
20
25
30
35
本底调查 1第 次跟踪 2第 次跟踪 3第 次跟踪 4第 次跟踪 5第 次跟踪
()
渔获种数种
游泳生物底栖贝类
Survey fishery species in Yangmeikeng reef
1.5 - 1.8 times
0
500
1000
1500
2000
2500
3000
3500
4000
4500
本底调查 1第 次跟踪 2第 次跟踪 3第 次跟踪 4第 次跟踪 5第 次跟踪
(kg/
km资源密度
2 )
总渔获游泳生物底栖贝类
0
50000
100000
150000
200000
250000
300000
350000
400000
450000
500000
本底调查 1第 次跟踪 2第 次跟踪 3第 次跟踪 4第 次跟踪 5第 次跟踪
(/k
m尾数资源密度尾
2 )
总渔获游泳生物底栖贝类
2.72 – 8.10 times
4.68 – 17.48 times
0
5
10
15
20
25
本底调查 1第 次跟踪 2第 次跟踪 3第 次跟踪 4第 次跟踪 5第 次跟踪
()
渔获种数种
0
5
10
15
20
25
30
本底调查 1第 次跟踪 2第 次跟踪 3第 次跟踪 4第 次跟踪 5第 次跟踪
(kg/
hm渔获率
2 h)
4.17 – 13.26 times
Gill net data;Total 75: 59 fish, 3 shrimp, 7 crab, 4 squila, 2 cephalopod
1.57 – 3.14 times
0
100
200
300
400
500
600
本底调查 1第 次跟踪 2第 次跟踪 3第 次跟踪 4第 次跟踪 5第 次跟踪
(/h
m尾数渔获率尾
2 h)6.16 – 13.04 times
Further analysis: Regression Tree will be used to analysis the catch data. – VERY VERY PRELIMINARY FOLLOW.
Yangmeiken Sampling areas (10-20 m depth)
? ? ? ?
? ?
? ? ?
? ?
? ? ?
大鹏澳
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
114º 30′ 114º 35′ 114º 40′ 114º 45′ E
亚
大
湾
深
圳
市
惠阳
市 惠
东
县
范
哑 铃 湾
和港
Dapeng Ao
HuiYang City
ShengZhen City
YaLing Bay
HuidongTown
114º 33′
22º 33′
114º 36′
22º 36′
调控礁区1
2
3
4
5
6
7
8
910 12
11
Sampling Station调查站位
礁区
杨梅坑Yangmeiken
? ? ? ?
? ?
? ? ?
? ?
? ? ?
大鹏澳
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
114º 30′ 114º 35′ 114º 40′ 114º 45′ E
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
114º 30′ 114º 35′ 114º 40′ 114º 45′ E114º 30′ 114º 35′ 114º 40′ 114º 45′ E
亚
大
湾
深
圳
市
惠阳
市 惠
东
县
范
哑 铃 湾
和港
Dapeng Ao
HuiYang City
ShengZhen City
YaLing Bay
HuidongTown
114º 33′
22º 33′
114º 36′
22º 36′
调控礁区1
2
3
4
5
6
7
8
910 12
11
Sampling Station调查站位
礁区
杨梅坑Yangmeiken
Yangmeiken Artificial reefs were deployed in 2008.
Both trawl and gillnet surveys were conducted before and after the effect.
2007: 1 survey (Apr)2008: 4 surveys (Mar, May, Aug, Nov)2009: 1 survey (May)
Sampling area Trawl Stations: 1, 4, 5, 6, 7 ,10, 11, 12
Gillnet Stations: 4, 7
Note: fishing activities are prohibited in reef areas. Survey was conducted near reef.
? ? ? ?
? ?
? ? ?
? ?
? ? ?
大鹏澳
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
114º 30′ 114º 35′ 114º 40′ 114º 45′ E
亚
大
湾
深
圳
市
惠阳
市 惠
东
县
范
哑 铃 湾
和港
Dapeng Ao
ShengZhen City
YaLing Bay
HuidongTown
114º 33′
22º 33′
114º 36′
22º 36′
调控礁区1
2
3
4
5
6
7
8
910 12
11
Sampling Station调查站位
礁区
杨梅坑Yangmeiken
? ? ? ?
? ?
? ? ?
? ?
? ? ?
大鹏澳
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
114º 30′ 114º 35′ 114º 40′ 114º 45′ E
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
22º 30′
22º 35′
22º 40′
22º 45′
22º 50 ′N
114º 30′ 114º 35′ 114º 40′ 114º 45′ E114º 30′ 114º 35′ 114º 40′ 114º 45′ E
亚
大
湾
深
圳
市
惠阳
市 惠
东
县
范
哑 铃 湾
和港
Dapeng Ao
ShengZhen City
YaLing Bay
HuidongTown
114º 33′
22º 33′
114º 36′
22º 36′
调控礁区1
2
3
4
5
6
7
8
910 12
11
Sampling Station调查站位
礁区
杨梅坑Yangmeiken
Sampling methodTrawl Gillnet
Identify species
All catch All catch
Sampling catch (in no and weight)
Most fish were 100% sampled or subsample (25%).Crustacean were either 100% sampled or subsampled (6%, 12.5%, or 25%)
100% sampled
Individual length and weight
Max and min Max and min
Trawl survey data
Gillnet survey data
Trawl survey data – Regression Tree
Fish sets (included all species)CPUE ~ Year + season + Station, CPUE=no/swept_area(km2)
S1,S4,S5,S7,S10,S11,S12
S1,S4,S5, S11,S12
S7, S10
S6
S6, 2007
S6 2008, 2009,Season 1, 2 ,3
S6 2008, 2009,Season 4
Fit all data (largest tree)
Cross-validation
Pruned tree based on the min deviance
Gillnet survey data – Regression Tree
S4
S4
S7, 2007
S7
S7, 2008, 2009,Season 1, 2
S7, 2008, 2009,Season 3, 4
Fit all data (largest tree)
Cross-validation
Pruned tree based on the min deviance
Fish sets (included all species)CPUE ~ Year + season + Station, CPUE=kg/swept_area(km2)
Conclusion
3
What will we get from the data?
Conclusion
Management measures were taken to protect the fishery resources – closed season, habitat enhancement, stock enhancement.
The catch of three species of fish increased after the manage measures were adopted.
Preliminary regression tree analyses also detect changes in catch associated with the implementation of habitat and stock enhancements. Further analyses on the full data set are required to look for benefits.
Additional modifications to the existing surveys may be required to collect necessary data to assess benefits (e.g. size data).
Work plan
4
What will we do next step?
Future work plan Complete paper describing fisheries management
in Guangdong Province – publish in scientific journal
Conduct additional data mining of the Guangdong Prov. artificial reef survey data as well as fishery data.
Extend Regression Tree analyses to determine effects of the adopted fisheries management measures (habitat and stock enhancement)
Publish results of analysis in scientific journal. Develop stock assessment models for reef
species in Guangdong province that specifically account for habitat and stock enhancements.
Bottlenecks Based on the Hawaii experience:
o Time – one month exchanges is not long enough to conduct the work. Exchanges should be three months.
o Support – sufficient financial support will be required to conduct exchanges.
o Data – a data exchange-sharing agreement should be established
o Monitoring – monitoring of existing reefs is not conducted. To conduct assessments a long-term monitoring program should be established.
Thanks!