Regional climate models and the coupling with marine biogeochemical models

Similar documents
Transient scenario simulations for the Baltic Sea Region during the 21st century

Phosphorus and Sulfur

Baltic Marine Environment Protection Commission

SWEDISH METEOROLOGICAL AND HYDROLOGICAL INSTITUTE

A simple scaling approach to produce climate scenarios of local precipitation extremes for the Netherlands

Welcome to the Understanding Dissolved Oxygen learning module. This section provides information on the following topics:

Leibniz Institute for Baltic Sea Research Warnemünde

South Africa. General Climate. UNDP Climate Change Country Profiles. A. Karmalkar 1, C. McSweeney 1, M. New 1,2 and G. Lizcano 1

REGIONAL CLIMATE AND DOWNSCALING

Chapter 55: Ecosystems

Looking beyond stratification: A model-based analysis of the biological drivers of oxygen depletion in the North Sea

LIMNOLOGY, WATER QUALITY

Current climate change scenarios and risks of extreme events for Northern Europe

Present trends and climate change projections for the Mediterranean region

Water Quality Modeling in Delaware s Inland Bays: Where Have We Been and Where Should We Go?

RECALLING Paragraph b of Article 13 of the Convention on the Protection of the Marine Environment of the Baltic Sea Area, 1974 (Helsinki Convention),

The Nitrogen Cycle. What is Nitrogen? Human Alteration of the Global Nitrogen Cycle. How does the nitrogen cycle work?

Hydrological and Material Cycle Simulation in Lake Biwa Basin Coupling Models about Land, Lake Flow, and Lake Ecosystem

THE WATER CYCLE. Ecology

Sensitivity of Baltic Sea deep water salinity and oxygen concentration to variations in physical forcing

BALTEX II Data Management and Baltic Grid: Status Report

Camilla Andersson, SMHI. ACCEPTED-projektet och resultat från andra Europeiska studier

METIER Course No. 6: Remote Sensing & Hydrosphere Helsinki 6 November 2008 Kati Tahvonen Finnish Environment Institute

Chapter 2. The Nitrogen Cycle

Biology Keystone (PA Core) Quiz Ecology - (BIO.B ) Ecological Organization, (BIO.B ) Ecosystem Characteristics, (BIO.B.4.2.

You are What You Eat

Guy Carpenter Asia-Pacific Climate Impact Centre, School of energy and Environment, City University of Hong Kong

How To Assess The Vulnerability Of The Neman River To Climate Change

Finnish Marine Research Infrastructure FINMARI

Aquatic Biomes, Continued

Phosphorus inputs to Lough Neagh. The increasing impact of agriculture

Selecting members of the QUMP perturbed-physics ensemble for use with PRECIS

Future Climate of the European Alps

Ecosystems. The two main ecosystem processes: Energy flow and Chemical cycling

Decadal predictions using the higher resolution HiGEM climate model Len Shaffrey, National Centre for Atmospheric Science, University of Reading

7.10 INCORPORATING HYDROCLIMATIC VARIABILITY IN RESERVOIR MANAGEMENT AT FOLSOM LAKE, CALIFORNIA

Michał Wierzbicki Department of Hydraulic Engineering Agricultural University of Poznań

EUROPEAN WATER RESOURCES AND POLICY

Algal Blooms, Circulators, Waterfowl and Eutrophic Greenfield Lake, NC. Michael A. Mallin, Matthew R. McIver, Ellen J. Wambach, and Anna R.

CLIMATE CHANGE, HUMAN SYSTEMS, AND POLICY - Vol.I - Effects of Global Warming on Marine Ecosystems - G.G. Matishov

Chesapeake Bay FieldScope Activity Teacher Guide

Eutrophication Status Report of the North Sea, Skagerrak, Kattegat and the Baltic Sea: A model study

II. Related Activities

Sweden s Commitment under the Baltic Sea Action Plan. Socio-economic inpact assessment

Washing our Dishes and Clothes without Polluting our Rivers and Seas

Real-time Ocean Forecasting Needs at NCEP National Weather Service

Sewerage Management System for Reduction of River Pollution

FRENCH ARCTIC INITIATIVE SCIENTIFIC PRIORITIES

NUTRIENTS AND EUTROPHICATION IN DANISH MARINE WATERS. Ministry of the Environment. Gunni Ærtebjerg, Jesper H. Andersen & Ole S.

Integrated Global Carbon Observations. Beverly Law Prof. Global Change Forest Science Science Chair, AmeriFlux Network Oregon State University

Environmental Science Scope & Sequence

Nitrogen Cycling in Ecosystems

Presented by Paul Krauth Utah DEQ. Salt Lake Countywide Watershed Symposium October 28-29, 2008

ENSO: Recent Evolution, Current Status and Predictions. Update prepared by: Climate Prediction Center / NCEP 29 June 2015

Climate Extremes Research: Recent Findings and New Direc8ons

STUDY GUIDE ECOLOGY. CHAPTER 21: Populations 1. An overview of ecology. Ecology is the study of interactions between organisms and their environment.

MEPC 56/23 ANNEX 2 Page 1 ANNEX 2 RESOLUTION MEPC.162(56) Adopted on 13 July 2007

Schools on Board Lab/Fieldwork Activity Example (As it appears in the Student Handbook!)

How To Manage Water Resources

Chesapeake Bay and Potomac Tidal Monitoring Programs Past, Present and Future

An Introduction to the Nitrogen Cycle

Hydrological transport modeling

Whale Jenga Food Web Game

Regionalizing global models:

Alpine Spring Festival

a. a population. c. an ecosystem. b. a community. d. a species.

Bio-optical monitoring of coastal Baltic Sea waters from research to applications

Coral Reefs Lecture Notes

RESTORATION AND ENHANCEMENT OF SOUTHERN CALIFORNIA LAGOONS

ENSO Cycle: Recent Evolution, Current Status and Predictions. Update prepared by Climate Prediction Center / NCEP 9 May 2011

Paleo-Earth System Modelling

FACTS ABOUT CLIMATE CHANGE

Climate Change: A Local Focus on a Global Issue Newfoundland and Labrador Curriculum Links

CIESIN Columbia University

HÄSSLEHOLM COMMUNITY MUNICIPAL OFFICE THE RESTORATION OF LAKE FINJASJÖN

TR Technical Report

Which of the following can be determined based on this model? The atmosphere is the only reservoir on Earth that can store carbon in any form. A.

Toxic Municipal Waste Water Treatment

What are the subsystems of the Earth? The 4 spheres

Biomes An Overview of Ecology Biomes Freshwater Biomes

Slide 1. Slide 2. Slide 3

Science to Support Nutrient Management in San Francisco Bay. David Senn San Francisco Estuary Institute

WFD and Sea of Marmara: a benthic perspective

2007 Pearson Education Inc., publishing as Pearson Addison-Wesley. The Jovian Planets

How to Generate Project Data For emission Rate Analysis

How To Understand And Understand The Effects Of Pollution And Water Quality

Long Term Challenges for Tidal Estuaries

Ginger Paige and Nancy Mesner University of Wyoming Utah State University

Observatory monitoring framework indicator data sheet

Swedish Sea Level Series. A Climate Indicator

How to measure Ammonia and Organic Nitrogen: Kjeldahl Method

WILLOCHRA BASIN GROUNDWATER STATUS REPORT

The Water Cycle Now You See It, Now You Don t

AIR TEMPERATURE IN THE CANADIAN ARCTIC IN THE MID NINETEENTH CENTURY BASED ON DATA FROM EXPEDITIONS

Name Date Hour. Plants grow in layers. The canopy receives about 95% of the sunlight leaving little sun for the forest floor.

Efficient Biomatement of the Baltic Sea - A Review

California Standards Grades 9 12 Boardworks 2009 Science Contents Standards Mapping

Projecting climate change in Australia s marine environment Kathleen McInnes

A Project to Create Bias-Corrected Marine Climate Observations from ICOADS

Nutrient bookkeeping in Germany why?

Transcription:

Regional climate models and the coupling with marine biogeochemical models H.E. Markus Meier Swedish Meteorological and Hydrological Institute, Norrköping and Stockholm University, Stockholm Markus.Meier@smhi.se ``Investigating harmful algae blooms in future climate of the Baltic Sea funded by Formas Cyanobacteria bloom 2005 Collaborators: Kari Eilola, Elin Almroth, Robinson Hordoir, Bengt Karlson, Per Hall (Göteborg University)

Threats for the Baltic Sea: 1. Eutrophication (increase in nutrients typically nitrogen or phosphorus) 2. Overfishing 3. Invasive species 4. Organic environmental poisons 5. Climate change 6. Oil discharges

The open Baltic Sea during the last 2000 years Andrén & Andrén, in manus

Regional climate modeling at SMHI Global Regional

Dynamical downscaling Add regional details (land-sea mask) Consistent scenarios using coupled models are needed

Regionalization is done for time- slices from GCMs Results archived from a GCM-run Regional simulations CO 2 Time 1800 1900 2000 2100 Present-day or a control climate Climate scenario (1961-1990) (2071-2100) 6

Mean maximum ice cover in control (blue) and scenario (red) (Meier et al., 2004) 7

winter spring Annual mean sea surface temperature change: + 2-4 C summer autumn Figure: Seasonal mean SST differences between the ensemble average scenario and simulated present climate (in C): DJF (upper left), MAM (upper right), JJA (lower left), and SON (lower right) (Meier, 2006).

(Source: Phil Graham, SMHI) -04-16

Salinity at Gotland Deep -04-16 Median profiles of salinity at monitoring station BY15 for present climate 1961-1990 (black solid line, shaded areas indicate the +/- 2 standard deviation band calculated from two-daily values for 1903-1998) and in projections for 2071-2100 (colored lines). In (a) only effects from wind changes are considered whereas in (b) projections based upon wind and freshwater inflow changes are shown. Numbers in the legend correspond to different scenario runs (Meier et al. 2006).

Sea surface salinity Present climate Projection with the largest change RCAO-ECHAM4/A2 5 psu

Coupling with a biogeochemical model

RCO-SCOBI High-resolution 3-D coupled physical-biogeochemical model for climate and process studies Sediment department N 2 Denitrification Nitrification O 2 H 2 S Denitrification Nitrification Ammonium adsorption Nitrogen fixation NO 3 NH 4 PO 4 Decomposition Assimilation Assimilation Assimilation Decomposition Burial NBT PBT From upper layer A1 A2 A3 Sedimentation To lower layer Grazing Mortality Predation Resuspension From upper layer DET Excretion Faeces Sedimentation To lower layer ZOO Grazing Pelagic variables: nitrate ammonium phosphate autotrophs (NO3) (NH4) (PO4) (A1,A2,A3) (diatoms, flagellates, cyanobacteria) zooplankton (ZOO) detritus (DET) oxygen (O2) Hydrogen sulfide (H2S) is included as negative oxygen. The sediment contains nutrients in the form of benthic nitrogen (NBT) and phosphorus (PBT). Aggregated process descriptions for oxygen dependent nutrient regeneration, denitrification and adsorption of ammonium to sediment particles as well as re-suspension and permanent burial of organic matter.

Long period experiment Forcing and model set-up of the 100 years model run RCO 6 N.m. run on the period 1902-1998 with reconstructed atmospheric forcing and river discharge data. Nutrient loading from land (rivers and coastal runoff) is based on climatological mean concentrations from the period 1970-1993. Point sources are based on HELCOM estimates from the 1990s. Atmospheric nitrogen deposition is based on HELCOM estimates from the 1980s and 1990s.

30-year mean and standard deviation (1969-1998) at Gotland Deep Observations Model Run 30

Oxygen, phoshate, nitrate at monitoring stations BY2, BY5, BY15, SR5 Run 45

Phosphate [μmol P/l] versus oxygen concentrations [ml O2/ l] at Bornholm Deep (BY5) and Gotland Deep (BY15) during 1969-1998: model results (black dots) and red dots (observations). Run 30

Monthly mean of observations (1990-2007) and model data (1980-1998) at Landsort Deep Run 45

Deviation from average area (10 5 km 2 ) 1,8 1,5 1,2 0,9 0,6 0,3 0,0-0,3-0,6 Maximum surface area covered by cyanobacteria 1982-1994 in the Baltic proper 1982 1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 Model results (blue), cumulative surface area estimated from satellite images (red) and the area corrected for unequal number of available images (brown; Kahru, 1997) Year Run 45

Scenario simulations

Scenario simulations of the marine ecosystem Important to assess uncertainties due natural variability, model biases from GCMs and RCMs, greenhouse gas emission scenarios, land use and sewage treatment scenarios, biogeochemical processes) To get robust information ensemble simulations should be performed

To estimate uncertainties an ensemble of 20 simulations has been performed: Four climate scenarios forced with two emission scenarios (A2, B2) and two GCMs: 1) ECHAM4/A2: SST +3.7ºC, SSS -3.2 psu, increased mixing 2) ECHAM4/B2: SST +2.9ºC, SSS -3.0 psu, increased mixing 3) HADAM3H/A2: SST +3.2ºC 4) HADAM3H/B2: SST +2.1ºC

To estimate uncertainties an ensemble of 20 simulations has been performed: Three nutrient load scenarios (Nest Institute, Stockholm University): 1) best case combining improved sewage treatment, P- free detergents and best possible agricultural practices (BC): P -21 000 t, N -150 000 t 2) Baltic Sea Action Plan (BSAP): P -15 000 t, N -133 000 t 3) Business as usual in agriculture (BAU): P +16 000 t, N +340 000 t

Mean oxygen profile at Gotland Deep Reference simulation (black) Run 45

Mean oxygen profile at Gotland Deep Reference simulation (black) and nutrient load scenarios BC, BSAP, BAU in present climate (solid lines) Run 45

Mean oxygen profile at Gotland Deep Reference simulation (black) and nutrient load scenarios BC, BSAP, BAU in present climate (solid lines) HADAM3H/A2 (2071-2100) (dotted lines) Run 45

Mean oxygen profile at Gotland Deep Reference simulation (black) and nutrient load scenarios BC, BSAP, BAU in present climate (solid lines) HADAM3H/A2 (2071-2100) (dotted lines) ECHAM4/A2 (2071-2100) (dashed lines) Run 45

Annual mean bottom oxygen concentration and changes [ml/l ] Reference (1969-1998) Best case BSAP Business as usual Present climate HADAM3H/A2 Run 45

Annual mean bottom oxygen concentration and changes [ml/l ] Reference (1969-1998) Best case BSAP Business as usual Present climate ECHAM4/A2 Note: colorbar Run 45

Annual mean phytoplankton concentration [mgchl/m 3 ] (0-10m) Reference (1969-1998) Best case BSAP Business as usual Present climate HADAM3H/A2 Run 45

Annual mean phytoplankton concentration [mgchl/m 3 ] (0-10m) Reference (1969-1998) Best case BSAP Business as usual Present climate ECHAM4/A2 Run 45

Summary 1 Projections of future climate suggest that water temperature may increase and ice cover may decrease In addition salinity may (or may not) decrease with reduced stability and deeper halocline (uncertainty caused by GCMs) The sensitivity of the highly non-linear biogeochemical response to climate change depends on key processes (e.g. in the sediments) that are not well understood (uncertainty caused by biogeochemical models) Oxygen concentrations of the surface layer may decrease In the southwestern Baltic phytoplankton concentrations may increase and there is a risk that cyanobacteria blooms become more intense

Summary 2 Future nutrient loads are uncertain due to unkown agricultural practices, sewage treatment, etc. The efficiency of the implementation of the BSAP may differ in future climate. However the BSAP will likely reduce the phytoplankton concentrations also in future climate (robust result) The business as usual in agricultural practices scenario in future climate may have larger impacts on the marine environment with increased phytoplankton concentrations than in present climate (robust result even when the bottom oxygen concentrations increase regionally)

Model hierarchy in ECOSUPPORT (Advanced modeling tool for scenarios of the Baltic Sea ECOsystem to SUPPORT decision making)

Model hierarchy in ECOSUPPORT (Advanced modeling tool for scenarios of the Baltic Sea ECOsystem to SUPPORT decision making) Transient simulations 1960-2100

Model hierarchy in ECOSUPPORT (Advanced modeling tool for scenarios of the Baltic Sea ECOsystem to SUPPORT decision making) Transient simulations 1960-2100 Multi-model ensemble approach

Model hierarchy in ECOSUPPORT (Advanced modeling tool for scenarios of the Baltic Sea ECOsystem to SUPPORT decision making) Transient simulations 1960-2100 Multi-model ensemble approach Higher trophic levels

Model hierarchy in ECOSUPPORT (Advanced modeling tool for scenarios of the Baltic Sea ECOsystem to SUPPORT decision making) Transient simulations 1960-2100 Multi-model ensemble approach Higher trophic levels Hot spots

Model hierarchy in ECOSUPPORT (Advanced modeling tool for scenarios of the Baltic Sea ECOsystem to SUPPORT decision making) Transient simulations 1960-2100 Multi-model ensemble approach Higher trophic levels Hot spots

Thank you for your attention! Cyanobacteria bloom 2008