Fly River, Papua New Guinea (eBook)
656 Seiten
Elsevier Science (Verlag)
978-0-08-055883-7 (ISBN)
In 1984 the Ok Tedi Mining Company Limited began mining copper and gold mineralisation from Mt. Fubilan, which is located at the headwaters of the Ok Tedi. In 1990, mining begin at the Porgera gold mine located at the headwaters of the Strickland River. Since that time both companies have intensely monitored the environment of the Fly River system in order to better understand the possible impact of mining.
This book is intended to assemble and summarise this vast amount of information, much of it contained in internal company reports, to better understand the environmental complexity and dynamics of this large and relatively undisturbed tropical river system.
The approach to be taken in achieving this outcome is to solicit contributions summarising each of the scientific disciplines to be covered from recognised experts with experience in the region.
* documents physical and biologic change in a large tropical river system brought about largely by mining in an otherwise pristine environment.
* this book brings together a broad rand of disciplines to provide a comprehensive overview of change in a complex and dynamical tropical river system based largely on previously unpublished company reports.
* the book provides examples of state-of-the-art strategies and methodologies for monitoring environmental impact in a large river system.
In 1984 the OK Tedi Mining Company Limited began mining copper and gold mineralization from Mt. Fubilan, which is located at the headwaters of the OK Tedi. Subsequent mining in the region followed in 1990. Since this time there has been intense monitoring of the environment undertaken by those in the field in order to better understand the possible impact of mining. This book assembles and summarizes research spanning two decades undertaken by leading experts with firsthand experience. Much of this research is contained in internal company reports, giving the reader rare insight and firsthand knowledge. - Documents physical and biologic change in a large tropical river system brought about largely by mining in an otherwise pristine environment- This book brings together a broad rand of disciplines to provide a comprehensive overview of change in a complex and dynamical tropical river system based largely on previously unpublished company reports- The book provides examples of state-of-the-art strategies and methodologies for monitoring environmental impact in a large river system
Front cover 1
The Fly River, Papua New Guinea: Environmental Studies in an Impacted Tropical River System 4
Copyright page 5
Contents 6
List of Contributors 14
Preface 18
Part 1. The Physical Environment 22
Chapter 1. Geomorphology, Hydrology, and Climate of the Fly River System 24
1.1. Introduction 24
1.2. Climate 26
1.3. River System Geomorphology 26
1.4. Hydrology 35
1.5. Geomorphic Changes Associated with Mining 46
References 68
Chapter 2. Texture, Geochemistry, and Mineralogy of Sediments of the Fly River System 72
2.1. Introduction 72
2.2. Texture of River Sediments 74
2.3. Metal Geochemistry of River-Deposited Sediments 89
2.4. Sediment Mineralogy 112
2.5. Conclusions 129
Acknowledgments 130
References 130
Chapter 3. The Rapid Spread of Mine-Derived Sediment across the Middle Fly River Floodplain 134
3.1. Introduction 134
3.2. Methods 137
3.3. Patterns and Rates of Floodplain Deposition of Mine-Derived Sediment 147
3.4. Discussion 163
3.5. Conclusions 166
Acknowledgments 167
References 167
Appendix: Results of Applied Particulate Level (APL) Annual Survey. Analyses are from Shallow Cores on the Floodplain and in Off-River Water Bodies (Sample Code Starts with W) 168
Chapter 4. Processes, Sediments, and Stratigraphy of the Fly River Delta 174
4.1. Introduction 174
4.2. Geologic Setting and Fluvial Characteristics 176
4.3. Delta Geomorphology 177
4.4. Hydrodynamics 180
4.5. Sediment Dynamics 182
4.6. Sediments and Stratigraphy 185
4.7. Shoreline Change Rates 191
4.8. Topics for Further Study 191
4.9. Conclusions 193
Acknowledgments 194
References 194
Chapter 5. Variable Styles of Sediment Accumulation Impacting Strata Formation on a Clinoform: Gulf of Papua, Papua New Guinea 198
5.1. Introduction 198
5.2. Background 200
5.3. Methods 204
5.4. Results 206
5.5. Discussion 211
5.6. Conclusions 220
Acknowledgments 221
References 221
Chapter 6. A Mass Balance for Sediment and Copper in the Rivers, Estuaries, Shelf and Slope of the Gulf of Papua, Papua New Guinea 226
6.1. Introduction 226
6.2. Methods 229
6.3. Results 235
6.4. Discussion 259
6.5. Conclusions 265
Acknowledgments 265
References 266
Part 2. Predicting the Impact of Mining on the Physical Environment 276
Chapter 7. Modeling the Impact of Tailings and Waste Rock Disposal on the Fly River System 278
7.1. Historical Background 278
7.2. Challenges in Modeling the Impact of the Ok Tedi Project 280
7.3. Predictions of Future Deposition, Water Level Change, and Inundation 301
7.4. Future Paths 306
References 307
Chapter 8. Floodplain Inundation Modeling and Forecasting for the Middle Fly 312
8.1. Introduction 312
8.2. Digital Elevation Data for the Floodplain - the Shuttle Radar Topography Mission (SRTM) 313
8.3. Floodplain Hydraulic Model - Development and Testing 321
8.4. Forecasting the Extent and Frequency of Floodplain Inundation 328
8.5. Results 330
8.6. Conclusions 336
Notes 337
References 338
Part 3. Copper Biogeochemistry, Bioavailability, and Toxicity 340
Chapter 9. Biogeochemistry of Copper in the Fly River 342
9.1. Introduction 342
9.2. Copper and Mine-Derived Suspended Sediment Distributions in the River System 344
9.3. Factors Affecting Copper Concentrations in the Fly River 346
9.4. Riverine Processes 355
9.5. Copper Cycling in Floodplain and Off-river Water Body Environments 365
9.6. Copper Cycling in the Fly River Estuary 371
9.7. Modeling of Copper Geochemistry 381
9.8. Overview 388
Acknowledgments 391
References 392
Chapter 10. Speciation, Bioavailability and Toxicity of Copper in the Fly River System 396
10.1. Introduction 396
10.2. Overview of Copper Speciation and Bioavailability 398
10.3. Bioassays 400
10.4. Historical Toxicity Monitoring Data in the Fly River System 405
10.5. Spatial and Temporal Trends in Copper Toxicity in the Ok TedisolFly River System 416
10.6. Risks to Aquatic Biota in the Fly River System 419
10.7. Looking Ahead 423
References 426
Part 4. Fish Biology, Assemblages, and Habitat 430
Chapter 11. The Biology of Barramundi (Lates calcarifer) in the Fly River System 432
11.1. Introduction 432
11.2. Stock Structure and Genetics 434
11.3. Life Cycle 435
11.4. The Fisheries for Barramundi 442
References 444
Chapter 12. Use of Changes in Fish Assemblages in the Fly River System, Papua New Guinea, to Assess Effects of the Ok Tedi Copper Mine 448
12.1. Introduction 448
12.2. Sampling and Analyses 451
12.3. Changes in Biodiversity 456
12.4. Changes in Fish Catch (Biomass) 470
12.5. Changes in Assemblage Composition 474
12.6. Conclusions 477
Acknowledgments 480
References 480
Chapter 13. Effects of Mine-Derived River Bed Aggradation on Fish Habitat of the Fly River, Papua New Guinea 484
13.1. Introduction 484
13.2. Study Area 488
13.3. Methods 489
13.4. Results 492
13.5. Discussion 494
Acknowledgments 504
References 504
Appendix 1: Measured and Derived Habitat Attributes Taken at Each Site to Provide an Indication of Fish Habitat Condition, Listing Parameter, Abbreviation, Units and Type (Reach or Point), with Correlation Coefficient and Significance Level for Spearman Rank Correlat 507
Part 5. Fauna, Vegetation, and Food Webs 512
Chapter 14. Insects of the Fly River System 514
14.1. Introduction 514
14.2. Beetles (Coleoptera) 517
14.3. Butterflies and Moths (Lepidoptera) 519
14.4. Flies and Mosquitoes (Diptera) 523
14.5. Cicadas and Other Hemiptera 524
14.6. Other Insects 526
14.7. Concluding Remarks 527
Acknowledgments 528
References 528
Chapter 15. Vegetation of the Ok Tedi-Fly River System 536
15.1. Introduction 536
15.2. Regional Vegetation 538
15.3. Plant Ecology 559
15.4. Summary and Conclusions 565
References 566
Chapter 16. Fauna and Food Webs of the Fly River Basin 570
16.1. Introduction 570
16.2. Habitats 572
16.3. Animal Groups 574
16.4. Food Webs and Functional Organization 586
16.5. Summary and Conclusions 590
References 592
Chapter 17. Development of Aquatic Food Web Models for the Fly River, Papua New Guinea, and their Application in Assessing Impacts of the Ok Tedi Mine 596
17.1. Food Webs and Their Use in Environmental Assessment 596
17.2. PreminesolEarly Mine Description of Food Webs 598
17.3. Use of Dietary Data in Food Webs 604
17.4. Use of Stable Isotopes to Describe Food Webs 612
17.5. Conclusions 630
Acknowledgments 631
References 632
Subject Index 637
Part 1. The Physical Environment
Chapter 1 Geomorphology, Hydrology, and Climate of the Fly River System
Geoff Pickup1,*, Andrew R. Marshall2
1 Consulting Geomorphologist, 1538 Sutton Road, Sutton, New South Wales 2620, Australia
2 Andrew Marshall & Associates Pty Ltd., 43 Warrangarree Drive, Woronora Heights, New South Wales 2233, Australia
* Corresponding author. Tel.: +61 26238 3427;
E-mail address: pickup01@westnet.com.au
Abstract
The Fly River occupies a large humid tropical drainage basin in western Papua New Guinea. In its upper reaches, the river system occupies steep mountain country but further downstream, there is a 500-km floodplain reach that is backed up by the Strickland. This chapter examines the climate, hydrology, and geomorphology of the system. It also describes the changes that have occurred in response to disposal of tailings and waste rock from the Ok Tedi mine. These include extensive deposition, especially in the upper part of the system, and rising water levels that have had a major effect on the floodplain.
1.1 Introduction
The Fly River system drains an area of about 75,000 km2 in western Papua New Guinea (Fig. 1.1). There are three major rivers in the system: the Ok Tedi, which drains the Hindenburg Ranges; the Upper Fly, which drains the southern part of the Victor Emanuel Range; and the Strickland, which drains the Victor Emanuel and Central Ranges. The Upper Fly and the Ok Tedi meet at D’Albertis Junction to form the Middle Fly, which meanders down a 400-km-long floodplain with extensive scroll bar complexes, cutoffs, and blocked valley lakes. The Middle Fly and the Strickland meet at Everill Junction before entering the Fly Delta. The delta covers about 10,000 km2 and extends downstream for another 400 km before entering the ocean in the Gulf of Papua. The Ok Tedi receives waste rock and tailings from Ok Tedi while the Strickland receives sediment load from mining operations at Porgera.
Figure 1.1 Location map. Mining operations at Tabubil and Porgera are shown by arrows.
This chapter covers the climate, geomorphology, and hydrology of the Fly. It examines rainfall distribution and basin hydrology. It describes the river system from the mountains to the lower end of the floodplain, including linkages between the river channel and the many off-river water bodies (ORWBs) in tributary valleys and on the floodplain. It concludes with a summary of mine-related impacts on the river system.
1.2 Climate
The Fly basin has a humid tropical climate. Average rainfall varies with elevation (Moi et al., 2001). Falls in excess of 10,000 mm/year occur at the Ok Tedi mine site (1,500–2,000 m), declining to about 8,000 mm/year along the upper and middle Ok Tedi. Further decreases occur downstream with values of 5,250 mm/year being recorded at Kuambit just downstream of D’Albertis Junction, 3,869 mm/year at Manda about two-thirds of the way down the Middle Fly floodplain, and 1,847 mm/year at Obo near Everill Junction. Heavy rainfall occurs throughout the year in the mountains, but there is a slightly less wet period from September to November. Seasonal variations are also stronger over the southern part of the floodplain, where rainfalls are lower than in the mountains.
Based on other stations in lowland Papua (McAlpine et al., 1975), annual evaporation is probably within the range 1,500–2,000 mm, which is less than annual rainfall in many areas.
Rainfall not only varies between seasons. The region experiences both El Niño and La Niña events, including severe drought episodes in 1972, 1983, and 1997. There may also be longer-term variations in rainfall. For example, Moi et al. (2001) report that rainfalls for 1999–2000 exceeded long-term averages across the region, with the largest percentage increases occurring in lowland areas.
The rainfall record for Tabubil, just below the mine site, shows some connection with the Southern Oscillation Index (SOI) (Fig. 1.2) but mainly during severe droughts. There is no obvious relationship at other times, making it difficult to use the SOI as a predictive tool.
Figure 1.2 Monthly rainfalls for Tabubil compared with the Southern Oscillation Index. Both datasets have been smoothed using a five-point moving average.
1.3 River System Geomorphology
In its upper reaches, the Ok Tedi and its tributaries drain a heavily dissected ridge and ravine landscape. The ridges rise to over 2,000 m in the north, but most of the basin lies between 200 and 800 m. The eastern part of the basin is karst country, including the massive Hindenburg Wall escarpment, and contains large areas of landslide debris and old debris flow deposits. In the west, igneous rocks are exposed on high mountains, but much of the area consists of shales, limestones, and sandstones. Slopes are unstable in spite of a dense rain forest cover, and landslides and debris flows are common.
Mine waste is disposed of into two tributaries of the Ok Tedi: Sulphide Creek (which joins the Ok Gilor, and then the Ok Mabiong in its lower section) and the Ok Mani (Fig. 1.3). These tributaries are referred as the Mine Area Creeks. These systems occupy steep, narrow valleys and, prior to mining, were cut down to bedrock for most of their length. Sediment deposits were restricted to local boulder chokes and short reaches with thin layers of armored cobbles. Sulphide Creek contains a waterfall, as does Harvey Creek, a small tributary of the Ok Mani that now receives waste rock from dumps on the southern side of the mine. These creeks are typical of the supply zone (Table 1.1) and were transporting virtually all delivered load before mining operations started.
Figure 1.3 A SPOT image of the Ok Tedi mine and the Mine Area Creeks.
Table 1.1 Classification scheme for river reaches on the Fly River System prior to mining
Source: Adapted from Pickup (1984) and Higgins et al. (1987).
The Upper Ok Tedi is a fast-flowing river capable of transporting large quantities of coarse sediment, including boulders. For much of its length, it occupies a bedrock gorge less than 200 m wide at its base, although there are wider sections with a few islands developing in the lower sections. Debris flow deposits flank the upper reaches of the gorge, and bed levels have fluctuated over time in response to massive landslides from the Hindenburg Wall and other areas, including one of 7 km3 about 8,800 BP (e.g., Pickup et al., 1979; Blong, 1991). Prior to mining, this reach of the river was classified as a supply zone (Table 1.1). However, unlike the Mine Area Creeks, the bed had a veneer of coarse sediment in transit, much of which probably came from the 1977 Hindenburg Wall landslide.
Just upstream from Ningerum, the Lower Ok Tedi emerges from its gorge into a gradually widening valley filled with what are probably Pleistocene alluvial deposits. These include weathered and indurated sand and gravel deposits topped by distinctive red soils. Initially, these “red beds” form valley edges and confine the channel but, as the valley widens, form terraces or terrace remnants, and the Ok Tedi develops a currently active floodplain within them. A braided channel develops, and forested islands have formed on some of the more stable braid bars. Before mining increased sediment input to the river, this reach was classified as an armored zone merging into a gravel–sand transition zone (Table 1.1). Finer material, including a large volume of sand, is now being deposited in this area.
Prior to mining, the armored zone ended upstream of the junction with the Ok Mart where braiding ceases, and there was a distinctive gravel front. Beyond this point, there was a gravel–sand transition zone (Table 1.1). Flow in the gravel–sand transition zone was (and still largely is) concentrated in a single channel, and meandering begins to develop. However, although there are several meander cutoffs and some channel traces, the floodplain is confined to a narrow belt, 1–4 km wide within the alluvial piedmont, and shows some traces of minor incision. The outer sections of some meanders also cut into Pleistocene terrace remnants, and lateral movement is restricted by indurated and highly weathered soils developed on former fluvial sediments.
The Middle Fly extends for about 420 km from D’Albertis Junction to Everill Junction, where it meets the Strickland. There are two distinct reaches: a sand zone and a backwater zone (Table 1.1). Prior to mining, the sand zone had a riverbed consisting of well-sorted fine-to-medium sand and extended as far downstream as Manda. This reach has a steeper water surface slope than the backwater zone that extends from Manda downstream to Everill Junction. The pre-mining backwater zone had a bed composed of mainly fine sand but with an increasing proportion of silt clay particles further downstream until less than 20% sand was present. A localized body of medium sand occurred downstream from Bosset and is probably associated with the slightly steeper river long profile there. It may have originated from the catchment...
Erscheint lt. Verlag | 9.1.2009 |
---|---|
Sprache | englisch |
Themenwelt | Sachbuch/Ratgeber |
Naturwissenschaften ► Biologie ► Ökologie / Naturschutz | |
Naturwissenschaften ► Geowissenschaften ► Geologie | |
Naturwissenschaften ► Geowissenschaften ► Hydrologie / Ozeanografie | |
Technik ► Bergbau | |
Technik ► Umwelttechnik / Biotechnologie | |
Wirtschaft | |
ISBN-10 | 0-08-055883-6 / 0080558836 |
ISBN-13 | 978-0-08-055883-7 / 9780080558837 |
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