Supervising Scientist, Darwin, 2005
ISBN 0 642 24395 6
ISSN 0 158-4030
- Table 2.1 - Ranger Production Activity For 2004-05 By Quarter
- Table 2.2 - Ranger production activity for 2000-2001 to 2004-05
- Table 2.3 - Annual Radiation Doses Received by Workers at Ranger Uranium Mine
- Table 2.4 - Ranger Minesite Technical Committee meetings
- Table 2.5 - Ranger Authorisation Changes/Approvals
- Table 2.6 - Summary of Magela Creek 2004–05 Wet Season Water Quality Upstream and Downstream of Ranger
- Table 2.7 - Summary of Gulungul Creek 2004–05 wet season water quality upstream and downstream of Ranger
- Table 2.8 Average Annual RDP Concentration at Jabiru East and Jabiru and Doses Received from the Inhalation of RDP at Jabiru
- Table 2.9 Jabiluka Minesite Technical Committee meetings
- Table 2.10 Jabiluka Authorisation Changes/Approvals
- Table 2.11 Summary of Ngarradj (Swift Creek) 2004–05 Wet Season Water Quality Upstream and Downstream of Jabiluka
- Table 2.12 Nabarlek Minesite Technical Committee Meetings
- Table 2.13 Nabarlek Minesite Technical Committee meetings
- Table 2.14 Nabarlek Authorisation Changes/Approvals
- Table 3.1 toxicity of Mg to six tropical freshwater species (a) without additional Ca and (b) with Ca added to maintain a Mg :Ca ratio of 9:1
- Table 3.2 predicted denudation rates on the Ranger landform
- Table 3.3 Influence of numerically-dominant fish species in channel billabongs upon correlation and regression results for the paired-site dissimilarity value, and time
- Table 6.1 - Overseas Events 2004-05
- Table 7.1 - Staffing numbers and locations (at 30 June 2005)
- Table 7.2 - Summary of Cost of Outputs
- Table 7.3 - Animal Experimentation Ethics Approvals
- Figure 1.1 Alligator Rivers Region
- Figure 2.1 - Ranger mine site
- Figure 2.2 - Water Treatment Plant under construction June 2005
- Figure 2.3 - Annual rainfall Ranger mine 1971–72 to 2004–05
- Figure 2.4 - Uranium concentrations in Magela Creek since the 2000–01 wet season (SSD data)
- Figure 2.5 - Uranium concentrations measured in Magela Creek by SSD and ERA during the 2004–05 wet season
- Figure 2.6 - Uranium concentrations measured in Magela Creek by SSD and ERA during the 2004–05 wet season
- Figure2.7 - Uranium concentrations in Gulungul Creek since the 2000–01 wet season (SSD data)
- Figure 2.8 - Uranium concentrations measured in Gulungul Creek by SSD and ERA during the 2004–05 wet season
- Figure 2.9A and 2.9B - Creekside monitoring results for freshwater snail egg production and larval black-banded rainbowfish survival for wet seasons between 1992 and 2004
- Figure 2.10 - Paired upstream-downstream dissimilarity values (using the Bray-Curtis measure) calculated for community structure of macroinvertebrate families in several streams in the vicinity of the Ranger uranium mine for the period 1988 to 2005
- Figure 2.11 - Paired control-exposed dissimilarity values (using the Bray-Curtis measure) calculated for community structure of fish in Mudginberri (‘exposed’) and Sandy (‘control’) billabongs in the vicinity of the Ranger uranium mine over time
- Figure 2.12 Relative abundance of fish in billabongs with different degrees of exposure to contaminants from Ranger uranium mine, 1993–2005
- Figure 2.13 Paired dissimilarity values (using the Bray-Curtis measure) calculated for community structure of fish in ‘directly exposed’ Magela and ‘control’ Nourlangie and Magela billabongs in the vicinity of the Ranger uranium mine over time
- Figure 2.14 Radon decay product concentration measured by eriss and ERA in Jabiru and Jabiru East from 2002 to early 2005
- Figure 2.15 View towards the former mineralised stockpile area and Interim Water Management Pond (Jabiluka, March 2005)
- Figure 2.16 Uranium concentrations in Ngarradj since the 1998–99 wet season
- Figure 2.17 Uranium concentrations measured in Ngarradj by SSD, DBIRD and ERA during the 2004–05 wet season
- Figure 2.18 Radium-226 activity concentrations in Ngarradj upstream and downstream of Jabiluka
- Figure 2.19 Radon decay product (RDP) and long lived alpha activity (LLAA) concentrations measured at the eriss Mudginberri Four Gates Rd radon station
- Figure 2.20 Radon flux densities from surfaces of the rehabilitated Nabarlek mine
- Figure 2.21 Gamma dose rates [ µGy-hr-1 ] measured at radiological anomalous area
- Figure 2.22 Heli-drilling pad in operation near Myra Falls Camp
- Figure 2.23 Extent of fire surrounding drill site as seen from the air
- Figure 3.1 Effect of Ca (expressed as Mg:Ca ratio) on the toxicity of Mg to three species, when Mg concentration was held constant at the IC50 concentration
- Figure 3.2 BurrliOZ species sensitivity distributions for Mg toxicity at (A) natural Magela Creek background Ca concentration (ie ~0.2 mg/L) and (B) a constant Mg:Ca ratio of 9:1
- Figure 3.3 Cumulative probability distributions for Mg concentration and Mg:Ca ratio in Magela Creek downstream of Ranger, from 1985–2005
- Figure 3.4 Radon exhalation measurements at the ore stockpile rim, using a radon emanometer
- Figure 3.5 222Rn flux density plotted versus the soil 226 Ra content for various sites
- Figure 3.6 Annual variation of 222 Rn flux density and cumulative rainfall plotted versus the date
- Figure 3.7 A freshwater mussel, Velesunio angasi, from the South Alligator River
- Figure 3.8 Areas of potential erosion / deposition on v3 landform after 1000 years using parameters for (a) ‘worst case’ scenario; (b) ‘best case’ scenario
- Figure 3.9 The Ngarradj catchment showing the Jabiluka Mineral Lease, eriss ’s gauging stations and local creek names
- Figure 3.10 Relative abundances of chequered rainbowfish and glassfish in channel billabongs over time
- Figure 3.11 Environmental correlates of rainbowfish abundance in Mudginberri Billabong, 1989–2005
- Figure 3.12 Temporal patterns of abundance of fish in shallow billabongs before and after the arrival of cane toads in two catchments
- Figure 3.13 Basic elements of a contaminant pathways conceptual model for Ranger uranium mine
- Figure 3.14 Conceptual model for transport of inorganic toxicants from Ranger uranium mine via a direct surface water to surface water pathway
- Figure 6.1 Two-way exchange of knowledge during the pop-netting program
- Figure 6.2 Communicating the water chemistry monitoring programme to Mudginberri residents
- Figure 6.3 Signing the Boggy Plain Memorandum of Understanding