3D Modelling of Combined Dredge and Disposal Plumes Dispersion. Mathews Morais

Similar documents
Monitoring of sediment dynamics during disposal of dredged harbour sediment in Port of Esbjerg, Denmark

Appendix O. Sediment Transport Modelling Technical Memorandum

12.0 COASTAL PROCESSES

APPENDIX O. Sediment Modeling of Dredging off Lelu Island, Prince Rupert, BC Canada, and Disposal of Dredgate at Brown Passage

PTM: A Lagrangian Particle Tracking Model. Joseph Gailani

Sediment Resuspension by Dredges: Defining the Issues

SUSPENDED SEDIMENT PLUMES ASSOCIATED WITH MECHANICAL DREDGING AT THE PORT OF OAKLAND, CALIFORNIA

Linking Sediment Transport in the Hudson from the Tidal River to the Estuary

A hydro-sedimentological view of the Samarco disaster, focusing in the Rio Doce estuary and adjacent coastal zone

Modeling of Dredging-Induced Sediment Resuspension: Remaining Questions and Progress Toward Answers

Predicting the Fate of Sediment Suspended Due to Dredging and Placement

Modeling Sediment Disposal in Inshore Waterways of British Columbia, Canada

Anderson-Ketron PSDDA Disposal Site Fate and Transport Modeling

Modeling plume from pipeline discharge of dredged material

SEDIMENT TRANSPORT IN RIVER MOUTH ESTUARY

Sediment Transport Modelling of Proposed Maintenance Dredging of the Outer and Inner Berths at the Aughinish Marine Terminal, Shannon Estuary

Modeling the Transport and Fate of Sediments Released from Dredging Projects in the Coastal Waters of British Columbia, Canada

Quantifying i the GLRI Metric for Annual Sediment Deposition in Great Lakes Harbors:

Lower Susquehanna River Integrated Sediment & Nutrient Monitoring Program

Appendix G.18 Hatch Report Pacific NorthWest LNG Lelu Island LNG Potential Impacts of the Marine Structures on the Hydrodynamics and Sedimentation

Applying Electrical Resistivity Methods for Measuring Dredged Material Density in Hopper Bins

Note: Deposition/dredging of tidal ferry channel in Dutch Wadden Sea Date: 23 June 2017

WIND EFFECTS ON CHEMICAL SPILL IN ST ANDREW BAY SYSTEM

THE SETTLING OF MUD FLOCS IN THE DOLLARD ESTUARY, THE NETHERLANDS

Appendix G.19 Hatch Report Pacific NorthWest LNG Lelu Island LNG Maintenance Dredging at the Materials Offloading Facility

IN SITU SPECIFIC GRAVITY VS GRAIN SIZE: A BETTER METHOD TO ESTIMATE NEW WORK DREDGING PRODUCTION

Sediment Transport and Strata Formation in the Adriatic Sea

Environmental Implications A Case Study

Three-Dimensional Numerical Modeling of Sediment Transport For Coastal Engineering Projects in British Columbia, Canada

Main issues of Deltas

Analysis of Sedimentation in Wonogiri Reservoir

Coastal and Hydraulics Laboratory

BEFORE THE ENVIRONMENTAL PROTECTION AUTHORITY AT WELLINGTON

SUBJECT INDEX. ~ ~5 physico-chemical properties 254,255 Redox potential 254,255

Sediment and Nutrient Mass Balance Model of Conowingo Pool

NASA Products to Enhance Energy Utility Load Forecasting

Earth Science Chapter 6 Section 2 Review

Coastal Sediment Properties and Longshore Sediment Transport

Typical Hydrologic Period Report (Final)

Particle Tracking Model Data Analysis Tools Part 2: Capabilities in SMS

June 2018 Sediments and Dredging at GBR Ports

Ocean Floor. Continental Margins. Divided into 3 major regions. Continental Margins. Ocean Basins. Mid-Ocean Ridges. Include:

Effectiveness of the mud motor near Koehool. Results and interpretion of a tracer study

27. Running Water I (p ; )

PRESENTATION TITLE. Regional Sediment Management Application of a Coastal Model at the St. Johns River Entrance BUILDING STRONG

Sedimentation in the Nile River

BEFORE THE ENVIRONMENTAL PROTECTION AUTHORITY AT WELLINGTON. of the Exclusive Economic Zone and Continental Shelf (Environmental Effects) Act 2012

UMCES Conowingo Studies Update November 4, 2015

Environmental impact assessment study of the new offshore dumping sites for Šventoji port in Lithuania

Annual transport rates at two locations on the fore-slope.

Restoration Goals TFG Meeting. Agenda

South Taranaki Bight Sediment Plume Modelling

Holderness Erosion and Evolution of the Spurn Peninsula

Density and Structure of the Earth

EVALUATION OF THE ADDAMS COMPUTER PROGRAM MODULES RELEVANT TO THE DISPOSAL OF MAINTENANCE DREDGING SPOIL FROM MARINAS AND SMALL BOAT HARBOURS

Sediment Connectivity and Exchange in Ameland Inlet

NUMERICAL ANALYSIS OF THE BED MORPHOLOGY IN THE REACH BETWEEN CABRUTA AND CAICARA IN ORINOCO RIVER.

Dynamic preservation of the coastline

PREDICTION ON MORPHOLOGICAL RESPONSE OF DREDGED SAND-BORROW PITS. Qimiao Lu 1 and Robert B. Nairn 1

Sedimentary Rocks Chapter 6

The Myanmar Mineral Exploration Handbook

Simulating Sediment Transport in the Patapsco River following Dam Removal with Dam Removal Express Assessment Model-1 (DREAM-1)

Chapter 8 Earth Systems and Resources

2. PRESENT CONDITION OF THE RESERVOIR 2.1 View of Wonogiri Reservoir (1/3)

Development, Testing and Application of the Multi-Block LTFATE Hydrodynamic and Sediment Transport Model

LAND AND OCEAN DISPOSAL OF SEDIMENTS DREDGED FROM MARINAS AND SMALL BOAT HARBOURS

Stream Discharge and the Water Budget

Fluid-Mud Deposits of the Lower Jurassic Tilje Formation, Offshore Mid-Norway By Aitor A. Ichaso and Robert W. Dalrymple 1

An Integrated Storm Surge, Hurricane Wave, Salinity and Sediment Transport Modeling System for Breton Sound, LA

STUDY AREA AND METHODOLOGY

Composition of the crust. Ore deposits. Ore distribution. Resources: Mineral resources. Reading: Today: Ch 12 (to p306)

Mineral resources. Composition of the crust. Resources: Reading: Today: Ch 12 (to p306) QUESTION Environmental Geology Mineral resources

Securing Manoeuverability of a Deep Draft Ship in a Sediment loaded Tidal River Berth

Decline of Lake Michigan-Huron Levels Caused by Erosion of the St. Clair River

Technical Memorandum No Sediment Model

Swift Creek Sediment Management Action Plan (SCSMAP)

8.1 Attachment 1: Ambient Weather Conditions at Jervoise Bay, Cockburn Sound

2018 Annual Review of Availability Assessment Hours

Cuyama Basin North Fork Vineyard

Tom Blackman Project Lead. Mékell Mikell Communications Representative

Location. Datum. Survey. information. Etrometa. Step Gauge. Description. relative to Herne Bay is -2.72m. The site new level.

7 EFFECTS ON COASTAL PROCESSES

Summary and status of the Reinfjord Exploration Project and other exploration targets within the Seiland Igneous Province

Mean (m/s) Maximum (m/s) Std. Deviation (m/s) December January March

Modelling vulnerability of coastal ecosystems to land-based mining pollution: a case study from Brazil

Location. Datum. Survey. information. Etrometa. Step Gauge. Description. relative to Herne Bay is -2.72m. The site new level.

U.S. Army Corps of Engineers Detroit District. Sediment Trap Assessment Saginaw River, Michigan

Estimation of Bed Load Transport in River Omi, South Western Nigeria using Grain Size Distribution Data

Details of data on Temperature, Relative Humidity, Rainfall and Wind are presented in the following sections.

Strategies for managing sediment in dams. Iwona Conlan Consultant to IKMP, MRCS

INDIANA HARBOR AND CANAL AIR MONITORING DATA ANALYSIS

The Marine Environment

ABP Southampton. Environmental Statement for Port of Southampton: Berth 201/202 Works. Appendix B. Dredge Material Characterisation

ABP Southampton. Environmental Statement for Port of Southampton: Berth 201/202 Works. Appendix K. Recommended Marine Conservation Zone Assessment

The Marine Environment

Aquatic Transfer Facility (ATF) San Pablo Bay (SPB) Proposed Region of ATF. Proposed Seabed Pipeline

Growing Strong Industries ~ Developing New Ideas ~ Nurturing Natural Resources

APPENDIX F SEDIMENT DEPOSITION AND HABITAT CONVERSION ANALYSIS

1) Executive Summary ) Metal Mines ) Petroleum Refining ) Pulp and Paper ) Thermal Generation ) Other...

Transcription:

3D Modelling of Combined Dredge and Disposal Plumes Dispersion Mathews Morais

About Vale Brazilian global mining company; Leader in the production of iron ore and the second largest producer of nickel; Operations exist in more than 30 countries over the five continents Products: Coal Copper Energy Fertilizers Iron Ore Logistics Manganese and Ferro-Alloys PGM & Precious Metals Steelmaking Nickel

Location The Amazon The Equator Sao Luis

Location Ponta da Madeira Pier IV

Preliminary dredge design Capex: 740,000 m 3 Opex: 177,000 m 3 /month

Environmental Requests What is the range of the plumes created at dredging and disposal sites? Pier IV What is the impact of those plumes? Fishing Zones

Sediment Properties 7 Fine Sand (0.13 ~ 0.25 mm) Very Fine Sand (0.063 ~ 0.13 mm) Silt and Mud (<0.063 mm) 20% 78% 2%

Field work 8

Ambient SSC Levels Average SSC level of 150 mg/l (dry season); Variation with tides and seasons in the range from 100 to 250 mg/l Based on UFMA and DTA measurements; 9

Ambient SSC Month Year DEPTH INSTITUTION TIDE Average Concentration (g/l) Feb-11 Near surface DTA 0.121 Feb-11 Mid-depth DTA 0.179 Feb-11 Near bottom DTA 0.153 Depth average Concentration (g/l) 0.151 Jan-13 Near surface UFMA Spring Low 0.137 Jan-13 Mid-depth UFMA Spring Low 0.143 Jan-13 Near bottom UFMA Spring Low 0.166 0.149 Jan-13 Near surface UFMA Spring High 0.144 Jan-13 Mid-depth UFMA Spring High 0.142 Jan-13 Near bottom UFMA Spring High 0.152 0.146 Apr-13 Near surface UFMA Spring Low 0.214 Apr-13 Mid-depth UFMA Spring Low 0.230 Apr-13 Near bottom UFMA Spring Low 0.235 0.226 Apr-13 Near surface UFMA Spring High 0.264 Apr-13 Mid-depth UFMA Spring High 0.254 Apr-13 Near bottom UFMA Spring High 0.212 0.243 Jul-13 Near surface UFMA Spring Low 0.106 Jul-13 Mid-depth UFMA Spring Low 0.131 Jul-13 Near bottom UFMA Spring Low 0.092 0.110 Jul-13 Near surface UFMA Spring High 0.210 Jul-13 Mid-depth UFMA Spring High 0.255 Jul-13 Near bottom UFMA Spring High 0.219 0.228

Acceptable SSC Levels British Colombia SSC to protect fish When ambient SSC is between 25 and 250 mg/l Maximum increase = 25 mg/l When ambient SSC > 250 mg/l Maximum increase is 10% of ambient Baird assumed Increases < 30 mg/l are considered insignificant Ambient SSC = 150 mg / l 11

Dredging Cycle Each dredge cycle 102 min for dredging 90 min for dump ~ 7.5 trips per day on average Average dredge volume per trip: 1,050 m 3 Average daily dredge capacity:~ 7,500 m 3 /day

Hybrid Modelling 1 - Plumes generated during dredging at Pier 4 MISED model 2 - Plumes generated by disposal of dredged material STFate (near-field) Plume dispersion driven by tidal currents 3 - Long-term fate of disposed materials due to sediment resuspension Morphological evolution Modelling Tasks Methodologies 13

STFATE Short-Term Fate of Dredged Material STFATE is the universal tool to: Provide deposition pattern and resuspension from placement, Manage placement sites, Regulatory Compliance (water column concentration), Evaluate environmental resource issues STFATE includes descent, dynamic collapse, bottom transport, and stripping phases 14

15 STFATE Model Setup 1-Duration of the disposal 2-10 min 2-Total number of bins Split dumping 3- Length of bin 50m (~160 ft) 4- Width of bin 13m (~42 ft) 5-Draft of loaded hopper dredge 4.5 m(~14.8 ft) 6-Draft of unloaded hopper dredge 1.8 m(~6 ft)

STFATE Sample Results 16

17 STFate Results Retro Area Sediment Mound thickness ~ flow velocity 0.6 0.5 STFate Results For Retro Area Sediment Mound Thickness 1200 1000 Maximum Bed Tickness (m) 0.4 0.3 0.2 0.1 Suspended Sediments Maximum Bed Tickness Total Suspended Sediment 800 600 400 200 Total Suspended (m 3 ) 0.0 0 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8 Depth Averaged Flow Velocity (m/s)

18 Overflow Sediment Properties (Choked Overflow) ( Measurements in August 2013 - Concentration) Location Sample Concentration (g/l) Retro Area Berth Pocket Overflow D1 3.9 Overflow D2 4.4 Overflow D3 3.4 Overflow D4 4.4 Overflow D5 3.4 Piér 4 P1 0.4 Piér 4 P2 0.4 Piér 4 P3 0.5 Piér 4 P4 0.4 Piér 4 P5 0.5

Model Results - Sediment Plume Generated by Dredging Activities Distribution of maximum predicted concentration with choked overflow Distribution of maximum predicted concentration for conventional overflow

Model Results: Combined Dredge and Disposal Plumes Dispersion

Model Results: Sedimentation at the Disposal Site

Conclusions Under current dredging practice the increase in ambient suspended sediment concentration is limited to the area around the dredge. Any increase in areas beyond Pier IV structure is insignificant; The influence of dredged material disposal activities is limited to 5 km to the north and 1 km to the south of disposal site, It was concluded that any impact of the dredge plume dispersion on sedimentation in the neighbouring areas would be insignificant and not measurable.

Obrigado, Thank you, Merci beaucoup!