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SLR Consulting (Africa) (Pty) Ltd
SLR Ref. 710.21002.00036 Report No.1
ENVIRONMENTAL IMPACT ASSESSMENT AND ENVIRONMENTAL MANAGEMENT PROGRAMME REPORT
FOR CHANGES TO OPERATIONS AT UMK MINE October 2017
Page L
APPENDIX L: STORM WATER MANAGEMENT REPORT
UNITED MANGANESE OF KALAHARI
SURFACE WATER MANAGEMENT REPORT
September 2017
PREPARED BY: PREPARED FOR:
AECOM SA (Pty) Ltd
2 Maryvale Road
Westville
3629
UMK (Pty) Ltd
95 Grayston Drive
Sandton
CONTACT PERSON CONTACT PERSON
Mr S Rasool Mr H Spangenberg
Tel No: 031 204 3800 Tel No: 011 2172800
TITLE : UNITED MANGANESE OF KALAHARI, SURFACE WATERMANAGEMENT REPORT
Project Team : AECOM (Pty) Ltd
Client : UMK (Pty)Ltd.
AECOM Project No : J00131-01
Status of Report : Final
AECOM Report No : J00131-01/07
Key Words : Stormwater Design, Stormwater Management , Catchment Areas
Date of this Issue : September 2017
For AECOM (Pty) Ltd
Compiled by : S. Rasool 08-09-2017
Initials & Surname Signature Date
Reviewed by : Kurt Hoffman 08-09-2017
Initials & Surname Signature Date
Approved by : D. Pillay 08-09-2017
Initials & Surname Signature Date
United Manganese of Kalahari Surface Water Management Report September 2017
TABLE OF CONTENTS Page No
1. INTRODUCTION ........................................................................................................................... 1
1.1 Location ....................................................................................................................... 1
1.2. Purpose of Report ....................................................................................................... 1
2. SITE CHARACTERISTICS ........................................................................................................... 1
2.1 Regional Climate .......................................................................................................... 2
2.2 Hour Rainfall ................................................................................................................ 3
2.3 Evaporation.................................................................................................................. 3
3. STORMWATER DESIGN .................................................................................................................. 3
3.1 Uncontaminated Stormwater / Clean Water (Minor Systems) ........................................ 4
3.2 Contaminated Stormwater/ Dirty Water (Major Systems) .............................................. 4
3.3 Stormwater Calculations .............................................................................................. 6
3.4 Primary Surface Water Storage Ponds ......................................................................... 8
3.5 Secondary Ponds ......................................................................................................... 9
4. CONCLUSION ............................................................................................................................ 12
5. REFERENCES ............................................................................................................................ 13
ANNEXURE 1 – BLOCK PLAN
ANNEXURE 2 – STORMWATER CATCHMENT AREAS
ANNEXURE 3 – TABLE 5-2 CLIMATIC SUMMARY TABLE FOR KURUMAN RAINFALL STATION
ANNEXURE 4 – TABLE 5-3 AVERAGE MONTHLY PRECIPITATION DATA
ANNEXURE 5 – FUTURE MINE LAYOUT
TABLE 1-1 WEATHER SERVICE STATION
TABLE 1-2 24HR RAINFALL DEPTHS (mm)
TABLE 1-3 ADOPTED AVERAGE LAKE EVAPORATION (mm)
FIGURE 1 - TYPICAL DETAIL OF TRAPEZOIDAL DRAIN
FIGURE 2 - TYPICAL DETAIL OF EARTH BERM
FIGURE 3 - TYPICAL CROSS-SECTION THROUGH MAIN ACCESS ROAD
FIGURE 4 - TYPICAL DETAIL OF CONTAMINATED STORMWATER POND
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1. INTRODUCTIONUnited Manganese of Kalahari (UMK) has appointed AECOM SA (Pty) Ltd. as the consultingcivil engineers, to undertake the surface water management design for the manganese plant.
1.1 Location
The site, which is approximately 300ha in extent, lies close to the existing MamatwanManganese Mine, just south of the town of Hotazal in the Northern Cape Province of SouthAfrica.
Facility X Y
UMK Mine 3 023 596.972 -11 291.340
See annexure 1 for Mine Layout.
1.2 Purpose of report
This report provides an overview of the planning and design of the surface drainagemanagement for this development, which includes both contaminated and uncontaminatedwater. Various catchment areas have been identified on the mine. See Annexure 2.
2. SITE CHARACTERISTICSThe site is relatively flat with a gentle slope towards the North West. The elevation on sitevaries from 1040m to 1100m above mean sea level. The highest topographical features(koppies and ridges) in the vicinity of the mine are the Korannasberg, approximately 13.75kmwest of the site, and the Kurumanheuwels, approximately 10km south east of the site.
The project area is bordered by two non-perennial drainage lines, namely the Witleegte(along the north eastern boundary) and the Gamogara (along the north western boundary).The Witleegte joins the Gamogara, just past the northern most corner of the project area (seeoverleaf). To the west of the site, lie several dry pans.
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2.1 Regional Climate (extracted from SRK Consulting: Smartt-Rissik Monthly WaterBalance update, dated September 2013)
Climate data for weather recording stations in the vicinity of the site was obtained from theSouth African Weather Services (SAWS) in Pretoria. The location and details of the stationused are detailed in Table 1-1. The long term rainfall record was abstracted from the Milnerstation while the Kuruman station data included more detail of the statistical informationregarding temperature, humidity, hail, fog and thunderstorms (this in not available at theMilner station).
Station Name Station Number Latitude Longitude Distance from Mining Area (km)
Milner 0393083_W 27 22 23 02 3.6
Kuruman 0393806 27 26 23 27 40
Table 1-1 Weather Services Station
Table 5-2 Climatic Summary Table for the Kuruman Rainfall Station (see annexure 3)summarises temperatures, precipitation and humidity. From the table it can be seen that thearea experiences an average maximum temperature of about 26 C and an average minimumtemperature of about 10 C. The area has experienced a maximum temperature of 39.9 C on02nd February 1988 and a minimum of -7.6 C on 14th June 1962.
The highest measure rainfall at the Milner station was recorded in the 1974/5 season, when900mm of rain fell. The lowest recorded annual rainfall was recorded in 1965/6, when 120mmfell. On the average the area experiences 27 days of thunderstorms and 1 day of fog throughthe year, while 1 day one of hail a year is recorded a year.
The humidity in the area ranges from 38% to 49% which is relatively low.
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Table 5-3 Average monthly Precipitation Data (see annexure 4) indicates the rainfall statisticsfor Milner station, which is 3.6km from site.
2.2 24 Hour Rainfall (extracted from SRK Consulting: Smartt-Rissik Monthly WaterBalance update dated September 2013)
24 hour rainfall depths, for various return periods were calculated from one day rainfallresults, obtained from Water research Commission (WRC) software developed in 2001, whichhas a database of rainfall stations records up to the year 2000. Table 1-2 below shows theMilner station, which is the nearest at approximately 3.6km from the mining site. The stationhas 67 years of recorded data that was used to generate the storm rainfall depths.
Return Period (1:x) yrs
Station Name Station Number 1:2 1:5 1:10 1:20 1:50 1:100 1:200
Milner 0393083 48 68 82 97 116 131 148
Table 1-2 24hr Rainfall Depths (mm)
2.3 Evaporation (extracted from SRK Consulting: Smartt-Rissik Monthly Water Balanceupdate dated September 2013)
The mine falls within the lower reaches of the D41K quaternary catchment. Evaporation datawas calculated from the Surface Water resources 1990 (Vol III)(WR 90). Table 1-3 belowshows the adopted average Lake evaporation.
Oct Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sep Total
Adoptedlakeevaporation
218 233 244 233 185 170 127 100 77 88 124 172 1971
Table 1-3 Adopted Average Lake Evaporation (mm)
3. STORM-WATER DESIGNDue to the nature of the operations on the mine, it is imperative that the stormwater bedivided into two categories, i.e. “Contaminated Stormwater”, and “UncontaminatedStormwater / Clean Stormwater”.
The clean and dirty water systems were designed, implemented and managed in accordancewith the provisions of Regulation 704, 4 June 1999 (Regulation 704) for water managementon mines.
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3.1 Uncontaminated Stormwater / Clean Stormwater (Minor System)
There are large areas within the site that will not be disturbed by the mining operations, andas a result, the stormwater runoff from these areas has not been concentrated (except for thepaved / roofed areas that constitute and relatively small percentage of this area) and henceshould not be contaminated. This water is hence categorised as UncontaminatedStormwater / Clean Stormwater.
These areas also include the paved areas of the main access road, product transport roadarea surrounding the waste area and facilities not directly linked to the mining operations, aswell as the railway siding, with exception to the loadout area. The stormwater runoffgenerated from these areas is intercepted, directed into and controlled by a series ofappropriately sized channels, v-drains and earth berms. Refer to Figure 1: Typical detail oftrapezoidal drain and Figure 2: Typical detail of earth berm.
This runoff is then discharged through 5m v-drain chutes, which in turn discharge at groundlevel onto designated open areas, or is dissipated as it has always done. As the climate isextremely arid, any resultant stormwater runoff which ponds in the small naturaldepressions will be allowed to evaporate into the atmosphere naturally.
The nature of this stormwater design philosophy is normally categorised as flows from theMinor System of a normal development, and as such, the respective elements of thestorm-water drainage system are designed for the 1:10 year storm frequency in terms of the“SA Guidelines for The Provision of Services in a Residential Township – “Red Book””. The“Red Book then defines the Major System and any major collector drain, canal orwatercourse that may traverse the site, and specifies a 1:50 year storm frequency for these.There are no such major drains, canals or watercourses that cross this site, hence, thetraditional Major System does not in reality exist on this site.
3.2 Contaminated Stormwater / Dirty Water (Major System)
Stormwater runoff that is categorised as contaminated, which is turbid and mineralised, is
intercepted in the design via a series of trapezoidal drains and contained within lined
“dirty” water dams. See Annexure 2.
The dirty water is controlled via earth berms, which consist of Kalahari sand, compacted to
98% MOD AASHTO in 200mm layers.
The flow of this water is controlled by trapezoidal drains varying from 0.5m to 1.0m deep,
which will be collected into ponds 1, 2, 3, 4, 5, 6, 7, 8, DS2, the Goba North and the Goba
South ponds respectively, and then will be allowed to evaporate, be pumped into the
Recycle Water Pond RW1 or into water tankers for dust suppression on the roads (only
water from mine pits are being used for dust suppression). Water entering the Goba North
and South ponds will have oil contamination from the Workshop areas, and hence, will firstly
pass through grease and oil traps at the building before discharging into the ponds.
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The nature of this contaminated stormwater design philosophy is categorised differentlyfrom the above Minor System and is viewed as being “akin” to a Major System as definedin the “Red Book”, due in this case mainly to the size of the contaminated areas (principallythe stockpiles) and also the nature of runoff from these areas, and as such, the respectiveelements of the storm-water drainage system are designed for the 1:50 year stormfrequency.
Stormwater runoff from the large disturbed plant area includes:
the stockpile yards;
crushers;
transfer towers;
mine pits;
screen house; and
silo.
Stormwater runoff from the minor disturbed plant area includes:
HDV wash-bay and workshop;
HDV parking;
4 Arrows contractor yard; and
Waste yard (waste area, prep lab and core yard).
Figure 1: Typical detail of trapezoidal drain
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Figure 2: Typical detail of earth berm
3.3 Stormwater Calculations
The uncontaminated stormwater / clean stormwater (Minor System) network has beensized, based on a 1 in 10 year flood event, covering mainly areas that have not beenhardened, resulting in accelerated runoff and also the relatively small roof areas, pavedroadways and parking areas. The design storm rainfall is derived from the depth-duration-frequency (DDF) relationships.
The rainfall intensity was calculated from the regional DDF equations representing the HRU1/78 DDF-relationships. (Noort and Stephenson, 1982)
For Inland Regions: I = (7.5 + 0.034MAP) T0.3 / (0.24 + td)0.89
Where,
I rainfall intensity (mm/hr);
T recurrence interval;
td stormwater duration (hr)
For the site, the nearest rainfall station, Milner (SAWB No.: 0393083), has a recorded meanannual precipitation (MAP) of 334mm and assuming a stormwater duration of 1.5hrs, thedesign rainfall intensity for the site has been calculated as follows:
I = (7.5 + 0.034*334)(10)0.3 / (0.24 + 1.5)0.89
= 23mm/hr
Thereafter, the Rational Method, with a runoff coefficient (C) of 0.7, was adopted to calculatethe maximum rate of discharge.
Rational Method:
Q = the maximum/peak rate of run-off
C = run-off coefficient
I = rainfall intensity
A = area of catchment in hectares.
The main access road has been designed with a 2.5% cross-fall with 1V in 2H bank and v-drain (Refer to Figure 3).
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Figure 3: Typical Cross-Section through Main Access Road
The contaminated stormwater / dirty stormwater (Major System) network has been sizedto prevent spillage more than once in 50 years (1 in 50 years) in accordance with Regulation704, with the design storm rainfall being derived from the depth-duration-frequency (DDF)relationships.
The rainfall intensity was calculated from the regional DDF equations representing the HRU1/78 DDF-relationships. (Noort and Stephenson, 1982)
For Inland Regions: I = (7.5 + 0.034MAP) T0.3 / (0.24 + td)0.89
Where,
I rainfall intensity (mm/hr);
T recurrence interval;
td stormwater duration (hr)
For the site, the nearest rainfall station, Milner (SAWB No.: 0393083), has a recorded meanannual precipitation (MAP) of 334mm and assuming a stormwater duration of 0.5hrs(30minutes), the design rainfall intensity for the site has been calculated as follows:
I = (7.5 + 0.034*334)(50)0.3 / (0.24 + 0.5)0.89
= 79.712 mm/hr
Where, Q= CIA/360
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AREA m² Hectare C I(mm/hr) Q=CIA/360(m³/s) Q(l/s)A1 45796 4.58 0.35 79.712 0.355 354.909A2 22034 2.20 0.35 79.712 0.171 170.759A3 19177 1.92 0.35 79.712 0.149 148.617A4 2923 0.29 0.35 79.712 0.023 22.653A5 33898 3.39 0.35 79.712 0.263 262.702A6 2868 0.29 0.35 79.712 0.022 22.226A7 11264 1.13 0.35 79.712 0.087 87.293A8 38437 3.84 0.35 79.712 0.298 297.878A9 1062 0.11 0.35 79.712 0.008 8.230
A10 65085 6.51 0.35 79.712 0.504 504.394A11 188755 18.88 0.35 79.712 1.463 1 462.809A12 57667 5.77 0.35 79.712 0.447 446.906A13 21975 2.20 0.35 79.712 0.170 170.301A14 7350 0.735 0.35 79.712 0.057 56.961A15 5561 0.5561 0.35 79.712 0.043 43.097A16 72435 7.2435 0.35 79.712 0.561 561.355A17 52491 5.2491 0.35 79.712 0.407 406.794A18 23303 2.3303 0.35 79.712 0.181 180.593
See annexure 2 for catchment areas.
3.4 Primary Surface Water Storage Ponds
Pond 1 is designed to contain a capacity of 5,408m3. It will accommodate surface water, fromrainfall and runoff, from the area next to the Primary Crusher (area 6) and the Loadout Silosupply conveyor, Transfer Tower 1 (TT1) and the Final Product Stockyard – (areas 7, 8 and 9which have a total catchment area of 54,052m2). A total of approximately 419 l/s of surfacerunoff will be accumulated and discharged into the pond. Areas 6, 7, 8 and 9 are connected tothis pond to through a culvert under the railway line.
Pond 2 is designed to contain a capacity of 1,352m3. It will accommodate surface water, fromrainfall and runoff, from the areas 2, 3 and 4 including the Screenhouse which have a totalcatchment area of 44,129m2. A total of approximately 342 l/s of surface runoff will beaccumulated and discharged into the pond.
Pond 3 is designed to contain a capacity of 1,250m3. It will accommodate surface water, fromrainfall and runoff, from the 6mm Stockpile Area (area 1 which has a total catchment area of45,796m2). A total of approximately 355 l/s of surface runoff will be accumulated anddischarged into the pond.
Pond 4 is designed to contain a capacity of 5,000m3. It will accommodate surface water, fromrainfall and runoff, from the Primary Stockyard Area (area 5), the HDV Wash-bay andWorkshop Area (area 14) and the HDV Parking Area (area 15). The surface water from thewash-bay and workshop and the HDV parking area will be pumped and discharged into thepond. These areas have combined catchment area of (46,388m2). A total of approximately360l/s of surface runoff will be accumulated and discharged into the pond.
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Pond 5 is designed to contain a capacity of 5000m3. It will accommodate surface water, fromrainfall and runoff, from the two future Stockpile Areas (areas 16 and 17 respectively) locatednear the Eskom substation area, which has a total catchment area of 124,926m2.A total ofapproximately of 968.149 l/s of surface water runoff water will be accumulated anddischarged into this pond. The pond will be located adjacent to the 6mm stockpile product.
Pond 6 is designed to contain a capacity of 5000m3. It will accommodate surface water, fromrainfall and runoff, from the Product Stockpile Area 1 (Area 10) and Mobile Crusher Area(Area 12), which has the total catchment area of 122,752 m2. A total of approximately951.301 l/s of surface runoff will be accumulated and discharged into the pond.
Pond 7 is designed to contain a capacity of 9400m3. It will accommodate surface water, fromrainfall and runoff, from the Product Stockpile Area 2 (Area 11) and the 4 Arrows ContractYard (Area 13) and the Waste Yard (Area 18) and has a total catchment area of 234,033m2.A total of approximately of 1813.704 l/s surface water runoff water will be accumulated anddischarged into this pond.
The contaminated stormwater trapezoidal drains have been sized to contain a minimum of a1:50 year storm for 30 minute duration and the contaminated stormwater ponds have beensized to contain a minimum of 2 No. of 1:50 year storms for 30 minute duration.
3.5 Secondary Ponds
North GOBA Pond - this is the lined pond as designed by GOBA to the north of the AdminOffices, Stores and Workshop that collects water from the building roofs and the surfacedplatform. (Note that the water that will be collected in this pond to the north will not beconsidered for recycling at this point, as the volume is limited and the pumping distance tothe Re-cycled Water pond, RW1 is considered to be too great and not cost effective),however, it has also been lined and is accessible to pump into a water bowser for dustsuppression on roads.
South GOBA Pond - this is the lined pond as designed by GOBA to the south of the AdminOffices that collects water from the Admin Building roof and the surfaced platform. (Note thatthe water that will be collected in this pond to the south will not be considered for recycling atthis point, as the volume is limited and the pumping distance to the Re-Cycled Water Pond,RW1 is considered to be too great and not cost effective), however, it has also been linedand is accessible to pump into a water bowser for dust suppression on roads.
DS2 will be the additional pollution control dam which will contain runoff from the FinishedProduct Stockpiles area and the loadout station in the event that Pond 1 is found to beinsufficient. This will be constructed west of the hammer sampler and load-out silo feedconveyor.
Mine Pit Water supply (MN1) is designed to contain a capacity of 2900m3. The water supplyfrom the J-Block Pit Area is inconsistent but can be substantial after heavy downpours.There is also a necessity to collect the water that may become trapped in the mine pits forenvironmental reasons. To this extent, water from the J-Block will be pumped out of the pitinto a silt trap and be collected in a HDPE lined pond (MN1). Thereafter, once operationsadvances, the MN1 pond will be backfilled and the water from J-Block will then be pumpedinto pond MN3 as mentioned below. Refer to Annexure 2.
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Mine Pit Water supply (MN2) is designed to contain a capacity of 27500m3. The watersupply from the Tree-Pit Area and the D-Block Pit Area is inconsistent but can be substantialafter heavy downpours. There is also a necessity to collect the water that may becometrapped in the mine pits for environmental reasons. To this extent, water from the two minespits namely D-Block and Tree Pit will be pumped out of the pits into a silt trap and becollected in a HDPE lined pond (MN2). Refer to Annexure 2.
Mine Pit Water supply (MN3) is designed to contain a capacity of 27500m3 .The watersupply from the J-Block Mine Pit is inconsistent but can be substantial after heavydownpours. There is also a necessity to collect the water that may become trapped in themine pit for environmental reasons. To this extent, water from the mine pit will be pumpedout of the pit into a sand trap and be collected in a HDPE lined pond (MN3). Refer toAnnexure 2.
The water from pollution control pond MN1, MN2 and MN3 will be pumped into water bowsersvia a submersible pump suspended from a bridge access gantry and used for dustsuppression around the site. This will only occur as and when there are heavy rainfall eventsor ponding in the pit occurs as a resultant of groundwater. Due to these events being of a lowfrequency or probability, permanent pumping lines are not included.
It is important to note that water from the mine pits will only be available after a significantrainfall event.
Recycled Water Pond (RW1) – the recycled water storage pond is constructed to store thewater from the Prentec plant after chlorination, the water from the Administration Block,Stores and Workshop roofs, including the LDV wash bay, the fuel store (after passing throughgrease traps) and their respective surfaced areas. This pond will be located to the northeastof the Prentec plant. A lay-by will be constructed near this pond to enable the filling of watertankers to be used for dust suppression along the haul road, the mine roads and the plantsroads.
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Figure 4: Typical detail of contaminated stormwater pond
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4. CONCLUSIONThe facets of engineering detailed in this report have been based on generally accepted
criteria, along with sound engineering principles and assumptions and conforms to Regulation
704.
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5. REFERENCES(i) The South African National Roads Agency SOC Limited, Drainage Manual, 6th Edition
(ii) SRK Consulting –SRK Consulting: Smartt-Rissik Monthly Water Balance update,dated September 2013)
(iii) Guidelines for the Provision of Engineering Services in Residential Townships (forthe Minor System design)
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ANNEXURE 1 BLOCK PLAN
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T
E
R
B
A
C
K
W
A
S
H
C
H
L
O
R
IN
A
T
IO
N
T
A
N
K
D
R
A
IN
3
x
1
1
0
m
m
C
A
B
L
E
S
L
E
E
V
E
S
3
x
3
S
T
A
C
K
B
O
X
3
x
3
S
T
A
C
K
B
O
X
S
O
L
E
N
O
ID
B
O
X
5
O
F
F
5
0
m
m
P
V
C
C
A
B
L
E
S
L
E
E
V
E
S
A
S
S
H
O
W
N
1
0
0
0
m
m
A
P
R
O
N
A
R
R
O
U
N
D
B
U
IL
D
IN
G
1
1
0
m
m
P
V
C
C
A
B
L
E
S
LE
E
V
E
S
D
U
M
P
1
1
1
1
3 x
1
10m
m
C
A
B
L
E
S
L
E
E
V
E
S
W
A
S
H
W
A
T
E
R
C
O
N
N
E
C
T
IO
N
W
A
S
H
W
A
T
E
R
C
O
N
N
E
C
T
IO
N1
1
W
A
S
H
W
A
T
E
R
C
O
N
N
E
C
T
IO
N1
W
A
S
H
W
A
T
E
R
C
O
N
N
E
C
T
IO
N
3
2
0
0
0
x
2
0
0
0
D
O
S
IN
G
B
U
IL
D
IN
G
4
S
1
9
S
2
0
1
B
A
R
S
C
R
E
E
N
S
C
R
E
E
N
/
D
E
-G
R
IT
T
E
R
P
L
A
N
T
P
R
E
N
T
E
C
S
E
W
E
R
T
R
E
A
T
M
E
N
T
1
1
0
Ø
H
D
P
E
TIE-INTO
PRENTEC
PLANT
RM3
RM4
RM5
1
1
0
Ø
H
D
P
E
S
L
U
D
G
E
D
R
Y
I
N
G
B
E
D
S
E
V
A
P
O
R
A
T
I
O
N
P
A
N
A
C
C
E
S
S
R
O
A
D
T
O
S
L
U
D
G
E
D
R
Y
I
N
G
B
E
D
S
P
R
O
P
O
S
E
D
N
E
W
7
5
m
m
H
D
P
E
P
U
M
P
I
N
G
L
I
N
E
2
1
3
3
E4
E1
E2
E3
P1
A3
P3
P4
S1
S2
S3
S4
S5
S6
S7
S8
N
E
W
P
U
M
P
C
H
A
M
B
E
R
P
O
S
I
T
I
O
N
PS1
PS2
PS3
T
U
R
N
I
N
G
C
I
R
C
L
E
PS4
I
S
L
A
N
D
3
m
G
R
A
V
E
L
R
O
A
D
3
m
G
R
A
V
E
L
R
O
A
D
F
1
F
2
F
3
F
4
F
5
F
6
F
7
F
8
F
9
F
1
0
F
1
1
F
1
2
F
1
3
F
1
4
F
1
5
F
1
6
F
1
7
F
1
8
F
1
9
F
2
0
F
2
1
F
2
2
F
2
3
F
2
4
F
2
5
F
2
6
F
2
7
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
G
A
T
E
F
E
N
C
E
L
I
N
E
F
E
N
C
E
L
I
N
E
F
2
8
F
2
9
F
3
0
F
3
2
F
3
1
3
.
0
0
1
.
5
0
3
.
0
0
A1
A2
R = 9.00 m
A4
A5
A6
3
.
0
0
A7
A8
A9
A10
A11
A12
A13
A14
A15
A16
A17
A18
A19
A
A
R = 9.00m
T
O
E
S
2
LC
LC
500m BLAST LINE
500m BLAST LINE
500m BLAST LINE
MAIN ROAD R380
MAIN ROAD R380
MAIN ROAD R380 / MAIN ACCESS ROAD INTERSECTION
MAIN ACCESS ROAD
HAUL ROAD
ROAD 1 TO ESKOM
SUBSTATION
CONVEYOR ROADS
& SERVICE ROADS
LINK ROAD BETWEEN HAUL
ROAD &
MAIN ACCESS ROAD
PLANT
ROAD 3
PLANT ROAD 3
PLANT ROAD 2
-6mm STOCKPILE
ESKOM SUBSTATION
P
R
I
M
A
R
Y
S
T
O
C
K
P
I
L
E
F
I
N
I
S
H
E
D
P
R
O
D
U
C
T
S
T
O
C
K
P
I
L
E
POSSIBLE FUTURE SINTER PLANT
SINTER YARD AND COKE
STORAGE
LOADOUT
STATION
-6mm LOADING
AREA
NEW RAIL LINE LOOP
TO HOTAZEL
H
A
U
L
R
O
A
D
POTABLE WATER TANKS
POND
NO.2
P
O
N
D
N
O
.:1
EARTH BERM
EARTH BERM
EARTH BERM
P
O
N
D
N
O
.
:
4
DIRTY
STORMWATER
DRAINS
DIRTY STORMWATER
DRAINS
POND
NO.:3
P
R
E
N
T
E
C
S
E
W
E
R
A
G
E
P
L
A
N
T
MAIN ACCESS ROAD
DIRTY STORMWATER
DRAINS
CONVEYOR ROADS
& SERVICE ROADS
EARTH BERM
EARTH BERM
DIRTY
STORMWATER
DRAINS
DIRTY STORMWATER
DRAINS
DIRTY STORMWATER
DRAINS
EARTH BERM
EARTH BERM
DIRTY
STORMWATER
DRAINS
EARTH BERM
EARTH BERM
HAUL ROAD
W
3
20
0m
m d
ia
H
DP
E C
la
ss 1
2
Min
1
.2
m C
ove
r
1
1
0
Ø
H
D
P
e
C
l
a
s
s
1
2
E15
1 x 3c /35mm² XLPE
1 x 1c /70mm² BCEW
NOTE 1
EH16
3
0
m
R=15m
S
T
O
P
ACCESS RAMP
FARM ROAD
L12
L13
L14
0 20
40
60
80
100
120
140
160
180
200 220 240 260 280 300 320 340 360 380 400 420 440 460 480 500
520
540
560
580
600
620
640
660
680
700
720
740
760
780
800
820
840
860
880 900 920 940 960 980 1000 1020 1040 1060 1080 1100 1120 1140 1160 1180 1200 1220 1240 1260 1280 1300 1320 1340 1360 1380 1400 1420 1440
1460
1480
1500
1520
1540
1560
1580
1600
1601.26
SEMH1
200Ø uPVC Cl 34
SEMH2
SEMH3 SEMH4
200Ø uPVC Cl 34
SEMH5
2
0
0
Ø
u
P
V
C
C
l
3
4
SEMH6
200Ø uPVC Cl 34
SEMH7
200Ø uPVC Cl 34
SEMH8
SEMH9
20
0Ø
u
PV
C C
l 3
4
SEMH10
2
0
0
Ø
u
P
V
C
C
l
3
4
SEMH11
2
0
0
Ø
u
P
V
C
C
l 3
4
SEMH12
2
0
0
Ø
u
P
V
C
C
l
3
4
SEMH13
2
0
0
Ø
u
P
V
C
C
l
3
4
S14
SEWER PUMP
STATION
200Ø uPVC Cl 34
200Ø uPVC Cl 34
2
0
0
Ø
u
P
V
C
C
l
3
4
1
1
0
Ø
H
D
P
E
TIE-INTO
PRENTEC
PLANT
RM3
RM4
RM5
1
1
0
Ø
H
D
P
E
TIE-IN FROM
PLATFORM
TIE-IN FROM
PLATFORM
TIE-IN FROM
PLATFORM
TIE-IN FROM
PLATFORM
TIE-IN FROM
WORKSHOP
VC 1
VC 2 VC 3
VC 4
P 1
P 2
P 3
P 4
F 1
F 2
F 3 F 4
F 5
F 6
F 7
F 8
F 9
1
PLAN
SCALE 1:100
14
10
10 10
10
10
14
19
22
2
2
20
20
7
7
16
24
25
26
15
32
27
9 32
27
32
28
29
16 17
20
36
EXISTING
PUMP
HOUSE
EXISTING
TANK 1
56m³
EXISTING
TANK 2
217m³
NEW
TANK 3
217m³
NEW
TANK 4
87m³
16
18
30
31 14
FOR FOUNDATION & EXCAVATION SETTING OUT
INFORMATION REFER TO DRAWING
A00003C210072002 & A00003C210072003
THE BOOSTER PUMP SET AND PIPEWORK WITHIN
THE PUMPSTATION SHALL BE DESIGNED, SUPPLIED
AND INSTALLED BY OTHERS.
PUMPSTATION ON HOLD. CONTRACTOR
TO BE APPOINTED IN THE CAPACITY OF
DESIGN AND CONSTRUCT
13
21
160mm Ø HDPE
PIPE LINE
200mm Ø HDPE
FIRE SUPPLY
PIPE LINE
160mm Ø HDPE
PIPE LINE
150mm Ø STEEL
PIPE LINE
EXISTING 110mm Ø
HDPE PIPE
EXISTING 200mm Ø
HDPE PIPE
EXISTING 160mm Ø
HDPE PIPE
TIE-IN 1
TIE-IN 2
TIE-IN 3
CONTRACTOR TO PROVE POSITION OF ALL EXISTING
PIPEWORK AND SERVICES. DIAMETER AND MATERIAL OF ALL
EXISTING PIPEWORK THAT WOULD BE CONNECTED / TIED INTO
WITH
NEW PIPEWORK SHALL BE CONFIRMED BY THE
CONTRACTOR. IF NECESSARY THE ENGINEER SHALL BE
CONSULTED FOR AMENDMENTS TO THE SCHEDULE OF
PIPEWORK.
100mm Ø HDPE SCOUR
PIPE LINE TO BE LAYED
500mm BELOW NGL.
10
34
34
33
33
25
26
35 35
37
32
PUMPSTATION
BY OTHERS
CONSTRUCT VALVE CHAMBER.
REFER TO DETAIL 1
CONSTRUCT VALVE
CHAMBER. REFER TO
DETAIL 1
14
100mm Ø HDPE SCOUR
PIPE LINE TO BE LAYED
500mm BELOW NGL.
B
A
F
E
NEW
FENCE
EXISTING FENCE
TO BE MOVED
FROM A - B TO E - F
C
D
EXISTING FENCE
TO BE REMOVED
REMOVE
EXISTING FENCE
14
35
21
35
EXISTING
OVERFLOW
CHANNEL
1000
H
NEW
FENCE
EXISTING FENCE
TO BE MOVED
FROM B - C TO G - H
G
500
14
35
EXISTING OVERFLOW CHANNEL TO BE
DEMOLISHED AND RECONSTRUCTED
TO SUITE SITE CONDITIONS
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
2
5
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
5
0
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
5
0
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
2
5
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
5
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
5
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
2
5
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
S
T
A
N
D
P
IP
E
S
T
A
N
D
P
IP
E
W
A
S
H
B
A
S
I
N
W
P
1
W
P
2
W
P
3
W
P
4
W
P
5
W
P
6
W
P
7
W
P
8
W
P
9
W
P
1
0
W
P
1
1
W
P
1
2
W
P
1
3
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
7
5
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
2
5
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
5
0
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
5
0
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
2
5
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
5
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
5
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
2
5
m
m
d
ia
H
D
P
E
C
la
s
s
1
2
S
T
A
N
D
P
IP
E
S
T
A
N
D
P
IP
E
W
A
S
H
B
A
S
I
N
W
P
1
W
P
2
W
P
3
W
P
4
W
P
5
W
P
6
W
P
7
W
P
8
W
P
9
W
P
1
0
W
P
1
1
W
P
1
2
W
P
1
3
1
1
0
Ø
H
D
P
E
TIE-INTO
PRENTEC
PLANT
RM3
RM4
RM5
1
1
0
Ø
H
D
P
E
MA
IN
A
CC
ES
S R
OA
D
MAIN ACCESS ROAD
MAIN ACCESS
ROAD
MAIN ROAD R380
MAIN ROAD R380
PRODUCT TRANSPORT
ROAD
TO KATHU
TO KURUMAN
ROADWAY
5m
20m
85m
5m5m
5m 5m
BIF PLATFORM
DS2
NEW 87m³
FIREWATER TANK
WITH BOOSTER
PUMP
NORTH
GATE
GUARD HOUSE FENCE
INSIDE EXPLOSIVE
YARD
1.5m
Sliding
Window
Toilet
with
Basin
3m
3m
2m
Guardhouse
on Concrete
Foundation
Fence as per SAP 412
Legislation
2m
2m
2m
1m Wide
Pedestrian gate
3.6 x 3.6 x 0.125m
Thick Concrete slab
See details
F5B
F5C
F5D
F5E
F5F
C1
C2C3
C4
7m
6m1m
0.3m
0.3m
200mm dia HDPE Class 12
1
6
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
1
1
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
WATER MAIN TAKE OFF POSITION
200m
m dia H
DP
E C
lass 12
1
6
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
1
6
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
1
6
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
110mm dia HDPE Class 12
1
1
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
1
1
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
200mm dia HDPE Class 12
160mm dia HDPE Class 12
1
1
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
1
6
0
m
m
d
i
a
H
D
P
E
C
l
a
s
s
1
2
W-3
W-3C W-3D W-3E W-3F W-3G
W-3A
W-3B
W-5
W-6
W-7
W-8
W-9
W-9A
W-9B
W-11
W-12
W-12A
W-12B
W-12C
W-12D
W-13
W-5A
W-5B
W-5C
W-14
W-15 W-15AW-16
W-14A
W-14C
W-14D
W-9C
W-10
W-14B
W-17
W-3C1
W-3C2
W-3D1
W-3E1
W-3A2
W-3A1
63
mm
d
ia
63mm dia 50mm dia
W-18
W-19
W-20
W-21W-22
HD
PE
C
la
ss 1
2
HDPE Class 12HDPE Class 12
160mm dia HDPE Class 12
W-5D
W-5E
W-5G
W-14E
W-14F
W-5F
W-5H
P
1
5
P
2
2
E
D
G
A
C
GV 1
GV 2
GV 3
GV 4
GV 5
GV 6
GV 7
GV 8
GV 9
W-24
W-25
W-26
W-27
W-28
W-29
W-30
W20
W1
200m
m dia H
DP
E C
lass 12
Min 1.2m
C
over
200m
m dia H
DP
E C
lass 12
Min 1.2m
C
over
END CAP
1
1
0
Ø
H
D
P
e
C
l
a
s
s
1
2
1
1
0
Ø
H
D
P
e
C
l
a
s
s
1
2
100mm VALVE AND
CHAMBER
TEMPORARY WATER
SUPPLY TO OFFICES
PIPE TO BE LAID AT A
MINIMUM OF 1m COVER
110x75mm TEE
75mm END CAP
110mm dia HDPE Class 12
Min 1.2m Cover
110mm dia HDPE Class 12
Min 1.2m Cover
75m
m dia H
DP
E C
lass 12
Min 1.2m
C
over
75m
m dia H
DP
E C
lass 12
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75m
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WORKSHOP 3- MECHANICAL
WORKSHOP 1- ELECTRICAL
1
2
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7
8
9
10
11
12
13
14
15
16
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35
36
37
38
39
40
41
42
43
44
45
46
47
68
67
66
65
64
63
62
61
60
59
58
57
56
55
54
53
52
48
49
50
51
01
02
03
04
05
06
07
08
09
10
11
12
13
34
33
32
31
30
29
28
27
26
25
24
23
22
21
20
19
18
14
15
16
17
PEDESTRIAN WALKWAY
COVERED
PARKING
(68 BAYS)
PEDESTRIAN WALKWAY
BUS BAY
TAXI RANK
V1
V2
V3
V4
V5
V6
V7
V8
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OVERFLOW AREA
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TO HOTAZEL
TO SISHEN
WM7.5RM8.5
TELEPHONE LINES
THROUGH LANE
BYPASS LANE
EXISTING ROAD EDGEEXISTING ROAD EDGE
TIED INTO EXISTING MAIN ROAD MR380
EXISITNG ROAD SURFACE
TO BE PAINTED
PROPOSED INTERSECTION ADJUSTMENTPROPOSED INTERSECTION ADJUSTMENT
TIED INTO EXISTING MAIN ROAD MR380
TURNING LANE
1:40 TAPERS
1:1
0 T
AP
ER
S
1:1
0 T
AP
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1:40 TAPERS
EXISITNG ROAD SURFACE
TO BE PAINTED
EDGE OF SHOULDEREDGE OF ROADEDGE OF SHOULDER
EDGE OF ROAD
BYPASS LANE
THROUGH LANEGM3.3
NEW ROAD EDGE
NEW ROAD EDGE
RAMP
WESTERN WEIGHBRIDGE
EASTERN WEIGHBRIDGE
3m LONG SOAKAWAYREFER TO DETAIL 2
1000l CALCAMITE SEPTIC TANK(REFER TO DETAIL 3)IL OF INLET PIPE = 1090.108
1 : 100 GRADE1 : 100GRADE
1 : 60 GRADE 1 : 80 GRADE
750mmØ PRECAST CONCRETE RINGMANHOLE (REFER TO DETAIL 4)
IL = 1090.218
RODDING EYEIL = 1090.333
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1000l CALCAMITE
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GRAVEL AREA
ELEVATED SECURITY VIEWING PLATFORM
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EARTH BERM
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EARTH BERM
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EARTH BERM
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FALLFALL
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SURFACE
CHANNEL TO
DISCHARGE ONTO
SURFACE
CHANNEL TO
DISCHARGE ONTO
SURFACE
P1
P2
P3
P4
P5
P6
P7
P8
P9
P10
P11
P12
R2 = 20m
R1 = 20m
R3 = 20m
P13
R4 = 11m
STAGING FOR 40 TRUCKS
D
.B
1
0
8
2
.
1
5
1
0
8
2
.
4
0
2
4
-
0
8
-
2
0
0
9
1
0
8
2
.
1
5
1
0
8
2
.
4
0
2
4
-
0
8
-
2
0
0
9
S
S
S
S
S
+
7
.
5
D
e
g
+
8
.
7
D
e
g
C
R
U
S
H
E
R
W
A
S
T
E
D
U
M
P
H
E
I
G
H
T
H
E
I
G
H
T5
.
4
M
6
.
6
M
B
e
r
m
0
.
7
8
m
B
e
r
m
0
.
9
3
m
B
e
r
m
0
.
9
2
m
B
e
r
m
1
.
0
4
m
B
e
r
m
1
.
3
8
m
B
e
r
m
1
.
3
7
m
6
.
5
D
e
g
4
.
8
D
e
g
H
37
1
1
34
35
16
17
GOBA SOUTH POND
PA
RK
IN
G
1413
15
18
19
N
E
W
R
E
C
Y
C
L
E
D
W
A
T
E
R
P
O
N
D
3C(1250m3)
GOBA NORTH POND
102
12
TRUCK STAGING LANES
1
2
3
POSSIBLE FUTURE
SINTER PLANT SIDING
1
31
30
20
21
22
3E
29
R
O
M
S
T
O
C
K
Y
A
R
D
36
3B (1352m3)
32
P
R
O
D
U
C
T
S
T
O
C
K
Y
A
R
D
33
6
5
3F
3A(5408m3)
3D
(5000m3)
25
8
26
7
9
24
23
28
27
D
U
S
T
S
U
P
P
R
E
S
S
IO
N
F
IL
L
IN
G
P
O
IN
T
4
M
IN
IN
G
C
A
M
P
1
G
O
O
S
E
N
E
C
K
ROAD BLOCKED HERE
52
ROAD FROM
HOLDING
CAMP
A0
UMK MANGANESE PROJECT - NORTHERN CAPE
BLOCK PLAN
THE MASTER HELD AT AECOM DURBAN BEARS THE ORIGINAL SIGNATURE OF APPROVAL
FOR INFORMATION
00 08/09/17 ISSUED FOR INFORMATION SR DP DP 201270383DP