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By: Douangkham Singhanouvong
Deputy Director of LARReC
Living Aquatic Resources Research Center (LARReC)))
American Fisheries society Conference
16-20 August 2015, Portland USA
1. Background
2. Methodology
3. Result
4. Conclusion
ï‚š Important fish migration take place in the Lower Mekong
River of southern Lao PDR during both the dry and wet
season.
ï‚š There are several fish species that migrate in both up and
downstream directions from the South to North all both
seasons.
ï‚š Lack of information about fish migration, fish abundant
and almost no quantitative data has been available for
future baseline monitoring.
ï‚š So, the Lee trap research has been started since 1993 - 98,
supported by IDRC, Canada.
ï‚š From 2007 to 2013 the study was supported by Fisheries
Programme of Mekong River Commission ( MRC)
Khong district
(Or Khong Island)
1.1 Location of study
Water Fall
1.2 Hoosom Yai channel (Con’t)
Lee traps or Bamboo -wing traps are one of
the most popular fishing gears in Laos
especially in Southern part. They are
made from Bamboo with the length of 8
to 10 meter and wide around 1.5 meter.
These gears are mainly used in the wet
season, set in appropriate channels and
placed in position to intercept the
nocturnal fish movement.
Lee trap are also placed directly in the
current with half of the bamboo matting
structure in the water, and half out
the water. These traps are caught
mainly fish that move up stream, when
they could not pass to the strength
current then they flow down into the
Lee trap (Singhanouvong. D, 1994).
An overall objectives
ï‚š To provide a time series of relative abundance
estimate for migratory white fish in the lower
Mekong River in order to monitor the effects of
fisheries management and basin development
activities.
1) To monitor and determine status and trends
in fisheries resources in terms of diversity and
relative abundance in the Khone Falls through
temporal and spatial variation.
2) To support valuable information on fisheries
resources for fisheries management and impacts
assessment purposes.
2.1. Data collection:
-Started from the end of May to the
September every year
-Count the number of fishing gear (lee
trap) that are working.
- Count the number and weigh of each
species caught for important species.
- Measurements of the mean flow
volume (m3/s) passing down HSY
- CPUE data recorded as
kg/trap/nightMeasured and weighted a fish
Year May June July August Sept
2007 17 17 0 0 0
2008 0 10 9 5 4
2009 17 18 10 7 7
2010 17 18 10 7 7
2011 21 22 10 2 3
2012 22 20 16 10 9
2013 21 21 16 7 6
3.1. Catch Per Unit Effort and trend ( 2007 to 2013)
3.2. CPUE top five species and trend (2007-2013)
Labeo chrysophekadion Pangasius larnaudiei
Hemisilurus mekongensis.
Bagarius yarrelli
Hemisilurus mekongensis
3.3. Fish biodiversity
3.4. Total fish landing by year (kg)
3.5. Total catch by month and year (kg)
Year May June July August Sep
2007 100,7 557 0 0 0
2008 0 682 1,176 887 69
2009 1,013 2,219 660 365 339
2010 80 594 2,214 974 501
2011 202 654 468 167 76
2012 544 1,000 429 449 284
2013 73 1,091 543 309 124
3.6. total catch by feeding type (%)
Carnivorous
Herbivorous
Omnivorous
Osteochilus microcephalus
Labeo chrysophekadion
Botia modesta
Pangasius conchophilus
Micronema sp
3.7. total catch by ecological characteristic
White Fish
Gray Fish Black Fish
Estuary Fish
‱ The daily catches in 2012 and
2013 were increased especially
during the high flow late May
and Early June.
‱ The number of fish species and
quantities of fish catch changes
from May to September.
‱ The main species reported in
the catch were :
Pangasius larnaudiei, Bagarius
yarrelli, Labeo chrysophekadion,
Pangasius conchophilus and
Hemisilurus mekongensis.
‱ The white fish were the dominant
species and follow by grey fish,
black fish and estuary fish
‱ The total catch from 2007 to 2013
varied depending on water flows.
‱ The highest catches were in 2009
and 2010 and the lower catches
were 2007 and 2011.
‱ The rainfall and water level were
perhaps the main factors affecting
fish catches.
‱ The Length frequencies of the main
five species shows not much
changed in term of length during
2008 to 2013.
‱ The results that we
have gathered can
now be applied to the
fisheries resources
management.
‱ This management is
important for the
Lower Mekong Basin
development planning
purposes.
Lee Trap Fisheries Monitoring in Southern Lao PDR

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Lee Trap Fisheries Monitoring in Southern Lao PDR

  • 1. By: Douangkham Singhanouvong Deputy Director of LARReC Living Aquatic Resources Research Center (LARReC))) American Fisheries society Conference 16-20 August 2015, Portland USA
  • 2.
  • 3. 1. Background 2. Methodology 3. Result 4. Conclusion
  • 4. ï‚š Important fish migration take place in the Lower Mekong River of southern Lao PDR during both the dry and wet season. ï‚š There are several fish species that migrate in both up and downstream directions from the South to North all both seasons. ï‚š Lack of information about fish migration, fish abundant and almost no quantitative data has been available for future baseline monitoring. ï‚š So, the Lee trap research has been started since 1993 - 98, supported by IDRC, Canada. ï‚š From 2007 to 2013 the study was supported by Fisheries Programme of Mekong River Commission ( MRC)
  • 5. Khong district (Or Khong Island) 1.1 Location of study
  • 7.
  • 8.
  • 9.
  • 10. 1.2 Hoosom Yai channel (Con’t)
  • 11. Lee traps or Bamboo -wing traps are one of the most popular fishing gears in Laos especially in Southern part. They are made from Bamboo with the length of 8 to 10 meter and wide around 1.5 meter. These gears are mainly used in the wet season, set in appropriate channels and placed in position to intercept the nocturnal fish movement. Lee trap are also placed directly in the current with half of the bamboo matting structure in the water, and half out the water. These traps are caught mainly fish that move up stream, when they could not pass to the strength current then they flow down into the Lee trap (Singhanouvong. D, 1994).
  • 12. An overall objectives ï‚š To provide a time series of relative abundance estimate for migratory white fish in the lower Mekong River in order to monitor the effects of fisheries management and basin development activities.
  • 13. 1) To monitor and determine status and trends in fisheries resources in terms of diversity and relative abundance in the Khone Falls through temporal and spatial variation. 2) To support valuable information on fisheries resources for fisheries management and impacts assessment purposes.
  • 14. 2.1. Data collection: -Started from the end of May to the September every year -Count the number of fishing gear (lee trap) that are working. - Count the number and weigh of each species caught for important species. - Measurements of the mean flow volume (m3/s) passing down HSY - CPUE data recorded as kg/trap/nightMeasured and weighted a fish
  • 15. Year May June July August Sept 2007 17 17 0 0 0 2008 0 10 9 5 4 2009 17 18 10 7 7 2010 17 18 10 7 7 2011 21 22 10 2 3 2012 22 20 16 10 9 2013 21 21 16 7 6
  • 16. 3.1. Catch Per Unit Effort and trend ( 2007 to 2013)
  • 17. 3.2. CPUE top five species and trend (2007-2013)
  • 18. Labeo chrysophekadion Pangasius larnaudiei Hemisilurus mekongensis. Bagarius yarrelli Hemisilurus mekongensis
  • 20. 3.4. Total fish landing by year (kg)
  • 21. 3.5. Total catch by month and year (kg) Year May June July August Sep 2007 100,7 557 0 0 0 2008 0 682 1,176 887 69 2009 1,013 2,219 660 365 339 2010 80 594 2,214 974 501 2011 202 654 468 167 76 2012 544 1,000 429 449 284 2013 73 1,091 543 309 124
  • 22. 3.6. total catch by feeding type (%)
  • 24. 3.7. total catch by ecological characteristic
  • 26. Gray Fish Black Fish Estuary Fish
  • 27. ‱ The daily catches in 2012 and 2013 were increased especially during the high flow late May and Early June. ‱ The number of fish species and quantities of fish catch changes from May to September. ‱ The main species reported in the catch were : Pangasius larnaudiei, Bagarius yarrelli, Labeo chrysophekadion, Pangasius conchophilus and Hemisilurus mekongensis.
  • 28. ‱ The white fish were the dominant species and follow by grey fish, black fish and estuary fish ‱ The total catch from 2007 to 2013 varied depending on water flows. ‱ The highest catches were in 2009 and 2010 and the lower catches were 2007 and 2011. ‱ The rainfall and water level were perhaps the main factors affecting fish catches. ‱ The Length frequencies of the main five species shows not much changed in term of length during 2008 to 2013.
  • 29. ‱ The results that we have gathered can now be applied to the fisheries resources management. ‱ This management is important for the Lower Mekong Basin development planning purposes.