Séminaire Indicang 18 et 19 mai 2005 Indicang – Interreg III Situation of European eel in the Oria river basin and progress of the project.

Slides:



Advertisements
Similar presentations
Information Needs for the Integrated F&W Program (ESA and Power Act) Jim Geiselman - BPA.
Advertisements

Group 1: Tonle Sap Location: Roberto 1.Mr. Carl Middleton 2.Mr. Chea Chan Tou 3.Mr. Eric Guerin 4.Mr. Ganesh Pangare 5.Mr. Hiek Sopheap 6.Mr. Hourt Khieu.
Non-native fish monitoring activities in Glen and Grand Canyons during 2000 Dave Speas, AGFD Carl Walters, UBC Scott Rogers, AGFD Bill Persons, AGFD.
PHYSICALLY BASED MODELING OF EXTREME FLOOD GENERATION AND ASSESSMENT OF FLOOD RISK L. S. Kuchment, A. N. Gelfan and V. N. Demidov Water Problems Institute.
Yakama Nation Pacific Lamprey Recovery Project Core Data And Monitoring Framework.
Fluidyn -FLOWSOL March D numerical simulation of surface flows.
Bay Scallop FMP Draft Amendment 1 Marine Fisheries Commission Aug. 12, 2010 Investigating Adaptive Management of Bay Scallop Harvest Based on Measures.
INDICANG - UK UK PARTNER - Westcountry Rivers Trust UK Project Manager - Dr Polly Bown.
GCSE Geography Enquiry
Are the apparent rapid declines in top pelagic predators real? Mark Maunder, Shelton Harley, Mike Hinton, and others IATTC.
Crest- highest part of a wave Trough- lowest part of a wave Wavelength- horizontal length between crests. Wave height- vertical distance from crest to.
Long-distance movements by flannelmouth sucker in big river habitats Matthew J. Breen & Trina N. Hedrick, Utah Division of Wildlife Resources.
Kinematic Routing Model and its Parameters Definition.
Continuous Hydrologic Simulation of Johnson Creek Basin and Assuming Watershed Stationarity Rick Shimota, P.E. Hans Hadley, P.E., P.G. The Oregon Water.
Wetlands. What is a wetland? There are three characteristics that describe a wetland: 1.Hydrology –There must be water at or near the surface of the land.
Water Resource Variability and Livelihoods in the Lower Rufiji Ecosystems (Tanzania) By Mwakipesile Augustino University of Dar es Salaam Tanzania
Opportunities for improving stock assessment Kristjan Thorarinsson Population Ecologist The Federation of Icelandic Fishing Vessel Owners.
Instream flow assessment in New Zealand. Flow assessment framework Morphology Evaluate for changes in flow Water quality Methods and parameters DO Temperature.
Importance of Protecting Lake Trout. 250,000 lakes in Ontario 1% of these contain lake trout Central/eastern Ontario has >1/3 of lakes Provincial responsibility.
A Perspective on Hydrologic Change in the Columbia River Basin David A. Jay OGI School of Science and Engineering Oregon Health & Science University, Portland,
American Samoa Ephraim Temple UH Sea Grant American Samoa Community College.
Climate Variability and Prediction in the Little Colorado River Basin Matt Switanek 1 1 Department of Hydrology and Water Resources University of Arizona.
SB4. Students will assess the dependence of all organisms on one another and the flow of energy and matter within their ecosystems. c. Relate environmental.
Noëlle BRU Laboratoire de Mathématiques et ses Applications UMR CNRS 5132 Université de Pau et des Pays de l’Adour  : Patrick PROUZET.
Oregon’s Likely Future Climate Predicted Rainfall Changes in Oregon PNW rainfall will be about the same or a little higher Source: Climate Impacts Group,
Measuring abiotic components  Objectives  To make an exhaustive list of abiotic factors  To discuss the ways they are measured  To critically appraise.
Hydrologic Statistics
The length structure of bigeye tuna and yellowfin tuna catch at different depth layers and temperature ranges: an application to the longline fisheries.
Adour basin INDICANG – 7-8 oct San Sebastian.
Ministry of Land, Infrastructure, Transport and Tourism Risk based Flood Management for adapting to Climate Change March 17, 2009 Toshio OKAZUMI Director.
Site Selection and Security Considerations Mark Heggli Innovative Hydrology, Inc. Consultant To The World Bank Expert Real-Time Hydrology Information Systems.
Population Dynamics Mortality, Growth, and More. Fish Growth Growth of fish is indeterminate Affected by: –Food abundance –Weather –Competition –Other.
Séminaire Indicang 18 et 19 mai 2005 Indicang – Interreg III UK PARTNER – Westcountry Rivers Trust UK Project Manager – Dr Polly Bown.
Study 466 Trawl Update Mt. Clemens Fisheries Research Station Prepared for the Saginaw Bay Coordination Meeting - Feb. 26, 2003 Spottail shiner.
Minho River PORTUGAL 2 nd Management Meeting of the INDICANG-35 project San Sebastian, 7-8 October 2004 Carlos Antunes & Alfredo Oliveira Centre for Marine.
Modeling the upper ocean response to Hurricane Igor Zhimin Ma 1, Guoqi Han 2, Brad deYoung 1 1 Memorial University 2 Fisheries and Oceans Canada.
Copyright © 2011 Pearson Education, Inc. The Simple Regression Model Chapter 21.
Biostatistics: Sampling strategies Data collection for fisheries assessment: Monitoring and sampling strategies.
Eel Fisheries-Recruitment-Future. Decline of Eel Populations??? Outside safe Biological limits? How are we influencing change? Can we manage the population.
Timeline Impaired for turbidity on Minnesota’s list of impaired waters (2004) MPCA must complete a study to determine the total maximum daily load (TMDL)
Séminaire Indicang 18 et 19 mai 2005 Indicang – Interreg III Situation of European eel in the Oria river basin and progress of the project.
26-28 May 2009Dr. Mala Supongpan Unusable Stock Recruitment Growth Natural Deaths Disease Emigration Immigration Recruitment Usable Stock Growth Natural.
EU management – current situation and future actions Kenneth Patterson European Commission Directorate-General of Fisheries and Maritime Affairs.
MINHO RIVER BASIN 1 st Seminar INDICANG, Rochefort, 18/05/2005 Minho River PORTUGAL Carlos Antunes, Alfredo Oliveira, Sérgia Costa Dias Centre for Marine.
GIANNOULAKI M., SOMARAKIS S., MACHIAS A., SIAPATIS A., PAPACONSTANTINOU C. Hellenic Centre for Marine Research, PO Box 2214, Iraklion 71003, Greece Department.
Fishing practise, science and management, a French case study Cédric Briand ÅLSEMINARIUM i Stockholm den 20 oktober 2005.
Physical and chemical factors affecting the upstream migration of amphidromous shrimp in the Luquillo Experimental Forest D.A. Kikkert, T.A. Crowl, and.
Seasonal variation in surface- groundwater exchanges in an urban floodplain with active gravel-bar formation Dorothea Lundberg Karen Prestegaard University.
Silver eel production indicators - Production d’anguille argentées Silver eel production indicators Eric Feunteun & Javier Lobon Cervia.
CPUE analysis methods, progress and plans for 2011 Simon Hoyle.
Figure 1. Map of the ONSR depicting the locations of the sampling sites and large springs (1-2 order magnitude). Discussion  SMB > Age-0 abundance is.
1 Optimizing sampling methods for pollutant loads and trends in San Francisco Bay urban stormwater monitoring Aroon Melwani, Michelle Lent, Ben Greenfield,
Piet Verdonschot Freshwater Ecology Group Group of Aquatic Ecology and Ecotoxicology Effects of wooded riparian zones on stream.
LONG-TERM PRAXIS OF FISHERY MANAGEMENT OF LAKE VÕRTSJÄRV AIN JÄRVALT Centre for Limnology Institute of Agriculture and Environmental Sciences Estonian.
Hypoxia Forecasts as a Tool for Chesapeake Bay Fisheries
Survey of Data Related to Municipal Water Systems in Utah
Brown Trout Growth: Growing, Growing, or Gone
Chapter 21: Movement of the Oceans
Rodney Govinden, Sabrena Lawrence, Maria Cedras, Kettyna Constance
Historic (post-European) Conditions
Maximum Sustainable Yield & Maximum Economic Yield
Review of the Mississippi Shrimp Fishery and a Look at the 2016 Season American Shrimp Processors Association Annual Meeting April 8, 2016.
Streams Hydrodynamics
Freshwater Systems = <1 % of Earth’s total water!
Presentation of the thematic groups
Jensen, et. al Winter distribution of blue crab Callinectes sapidus in Chesapeake Bay: application and cross-validation of a two-stage generalized.
Dams Helpful or Hurtful?.
Ocean Movements 15.3.
The Eel’s Amazing Migration: A Focus on the Adult Spawning Run
하구및 연안생태Coastal management
Presentation transcript:

Séminaire Indicang 18 et 19 mai 2005 Indicang – Interreg III Situation of European eel in the Oria river basin and progress of the project

Séminaire Indicang 18 et 19 mai 2005 Characteristics of the basin : - Valleys fit in V people through river axis - Maximum height: m - Mean Temperature: 12,4 ºC - Mean rainfall: mm - Mean basin discharge: 942 hm 3 /year - Length: 75 km Item Zero

Séminaire Indicang 18 et 19 mai 2005 Eel fisheries in the basin - Launch of fisheries monitoring plan New regulation issued Agreed with the fishermen. License and daily catches report - Decline in the stock: intuitively, no any historical data series. - More than a century of fishery activity and sale. Item Zero

Séminaire Indicang 18 et 19 mai 2005 Situation of the habitat -10 Native or non defined origin fish species, 3 introduced fish species - 24 % of total riverbank affected by hard bank reinforcement - More than 100 obstacles, 1-3 m high Item Zero - Poor habitat quality - Poor water quality in general, pollution

Séminaire Indicang 18 et 19 mai 2005 Item Zero Distance to mouth (km)) Eels/1000 m Yellow and silver eel abundance and distribution in Oria Basin

Séminaire Indicang 18 et 19 mai 2005 Catches report 2003/2004 Validation with samplings and data of distribution companies Lack of precision of data Underestimation of catches It is obligatory to deliver the catches report to obtain the new license. Apply it. Low response Data from 40,3% of fishermen SolutionsProblems First time we have data! Results glass eel

Séminaire Indicang 18 et 19 mai 2005 Description of fisheries 2003/ Fishermen/gear - More fishermen in January - More fishermen in boat and sieve Results glass eel

Séminaire Indicang 18 et 19 mai 2005 Description of fisheries 2003/ Catches/Fishing effort - Significant differences in CPUES among fishing gears (p=0,0003), higher in boat and sieve - -Highest CPUEs in December but no significant differences among months in each modality Results glass eel

Séminaire Indicang 18 et 19 mai 2005 Description of fisheries 2003/2004 preliminary approach Stepwise forward multiple regression Sieve land fishing: p=0, r 2 =.471 n=79 Independent variables: Days before new moon Days of fishing season Catch=91606,8-205,04*days of fishing season-599,67*days before new moon+ 6990,* High tide level-6952,37*Temperature in depth- Precipitation*117, ,184* N component wind Catch/day: Precipitation Flow Turbidity Water temperature Air temperature High tide level Temperature in depth N component wind E component wind Swell period E component deep current N component deep current Marine variables: River variables: Catch=14424,8-28,01*days of fishing season-104,334*days before new moon+ 725,09* High tide level-1022,3* Temperature in depth+7.13*Turbidity Boat fishing: p=0, r 2 =.545 n=87 Results glass eel

Séminaire Indicang 18 et 19 mai 2005 Experimental samplings - With a motor boat, two fishermen and two sieves of 1.60 diameter (surface and depth) - Just three samplings because: - Temperature, salinity, turbidity, water current speed - In the mouth - Upstream - Samples given by the fishermen - Only when high entrance: change of strategy - started in December No validation Results glass eel

Séminaire Indicang 18 et 19 mai 2005 Experimental samplings -According to the pigmentation levels glass eels are in a more advanced stage upstream as we expected VA VB VIA0 VIA1 VIA2 In the mouth Upstream - Comparison of mouth and upstream glass eels 0,070,090,110,130,150,170,19 Log (weight+1) 0,78 0,81 0,84 0,87 0,9 0,93 Log (size) Upstream: Log (size) = -0, ,802235*Log(weigth+1) r 2 =.883 Mouth Log (size) = -0, ,65796*Log(weigth+1) r 2 =.748 -No significant differences between size/weight relations (ANCOVA p=0.0764): NO SLIMMING Results glass eel

Séminaire Indicang 18 et 19 mai 2005 Experimental samplings - Trap: Installation of a gadget to keep clear the entrance Leafs obstruct the entrance  ????  To increase the ramp High flow variability:  Flooding and silting  Not enough water to reach the base of the sample. SolutionCause It has just worked properly in 25 % of the days (just one sample obtained): No validation this year Results glass eel

Séminaire Indicang 18 et 19 mai ,5 KmSan PedroDesemb. San Pedro6 4 KmSan PedroA. ab. Andatza5 25 KmLeitzaranOlazar4 23 KmLeitzaranLeitzaran Andoain3 22 KmOriaAndoain2 15 KmOriaZubieta1 Distance to mouth RiverStationNº Specific sampling stations 2004 Results yellow and silver eel

Séminaire Indicang 18 et 19 mai passes- Carle & Strub (1978) (MEMAPO) ZubietaAndoain Leitzaran Andoain Leitzaran Olazar S.P. Andatza S.P. Desemb. Width (m) Depth (cm) C1C C2C C3C CTCT Ninf./Ha N/Ha Nsup./Ha Var (N) P χ2χ g.l. 1; χ 2 0, valid.Var (N) > Zubieta: no constant catchability Leitza Olazar : no valid sampling Results yellow and silver eel

Séminaire Indicang 18 et 19 mai 2005 Leitzaran Olazar : no valid sampling In stations with high catchability the estimations are better when passing three times Zubieta: valid sampling but underestimated (see 3 passes) Results yellow and silver eel

Séminaire Indicang 18 et 19 mai 2005 Density decrease, 3 dams between the two points Results yellow and silver eel

Séminaire Indicang 18 et 19 mai Length (cm) % num. Eel population structure. Olazar station. Leitzaran river. Summer eels /Ha – Distance to mouth:25 Km Length (cm) % num. Eel population structure. Leitzaran station. Leitzaran river. Summer eels /Ha – Distance to mouth:23 Km Strong decrease between 1,5 and 2kms. A nearly insuperable dam. Upstream few eels and the population structure does not fit to this point Results yellow and silver eel

Séminaire Indicang 18 et 19 mai 2005 Stream that flows in the estuary with high recruitment Length (cm) % num. Eel population structure. Ab. Adantza station. San Pedro river. Summer eels /Ha – Distance to mouth4 Km. Eel population structure. San Pedro station. San Pedro river. Summer Length (cm) % num eels /Ha – Distance to mouth1,5 Km Results yellow and silver eel

Séminaire Indicang 18 et 19 mai The stations with higher area and depth (Zubieta, Andoain, Olazar): -The stations with lower area and depth (S.P. Andatza, S.P.Desem- bocadura, Leitzaran Andoain): - Litter stations: 3 passes -Low catchability, when passing two times population underestimated (sometimes even with three) - High catchability, passing three times better estimations than with two, tighter confidence limits Bigger stations: what method would fit better in these cases? Results yellow and silver eel