GEO PROJECT 1 DECLARATION 2 INTRODUCTION SITE DESCRIPTION The approximate location of the site is 29°52'39.3"S (-29.8775700°) 26°24'42.5"E (26.4118000°). Lying even further east of Pretoria than Silver Lakes, the site is situated right out in the 'country', a burgeoning neighbourhood that started with a series of smallholdings and country estates and is fast becoming something of a suburb, with beautiful views and any number of hiking opportunities. Spatially heterogeneous landscapes provide larger habitat variations than a spatially homogenous landscape, and thus the importance of ridges as biodiversity hotspots cannot be replicated. Spatially, the orientation of ridges is important. The orientation of the ridge in relation to the sun will influence the vegetation composition on the different sides of the ridge, since the duration of daylight varies according to the spatial aspect of the ridge. The orientation of the ridge will also influence the rainfall pattern across the ridge. The geology and erodibility of the soils, as well as the slope, will influence the water velocity, retention and nutrient leaching rates. Proposed site CLIMATIC AND TOPOGRAPHIC DATA At Pretoria, the summers are long, warm, and partly cloudy and the winters are short, cold, dry, and clear. Over the course of the year, the temperature typically varies from 42°F to 83°F and is rarely below 36°F or above 90°F.Based on the tourism score, the best times of year to visit Pretoria for warmweather activities are from late February to mid-May and from mid-August to late October. 3 Average Temperature at Pretoria The warm season lasts for 5.9 months, from September 24 to March 20, with an average daily high temperature above 79°F. The hottest month of the year at Pretoria is January, with an average high of 83°F and low of 64°F. The cool season lasts for 2.1 months, from May 27 to July 31, with an average daily high temperature below 69°F. The coldest month of the year at Pretoria is June, with an average low of 43°F and high of 66°F. Clouds At Pretoria, the average percentage of the sky covered by clouds experiences significant seasonal variation over the course of the year. The clearer part of the year at Pretoria begins around March 28 and lasts for 6.4 months, ending around October 10. The clearest month of the year at Pretoria is July, during which on average the sky is clear, mostly clear, or partly cloudy 92% of the time. The cloudier part of the year begins around October 10 and lasts for 5.6 months, ending around March 28. The 4 cloudiest month of the year at Pretoria is November, during which on average the sky is overcast or mostly cloudy 36% of the time. Precipitation A wet day is one with at least 0.04 inches of liquid or liquid-equivalent precipitation. The chance of wet days at Pretoria varies very significantly throughout the year. The wetter season lasts 5.5 months, from October 17 to April 1, with a greater than 26% chance of a given day being a wet day. The month with the wet days at Pretoria is December, with an average of 15.6 days with at least 0.04 inches of precipitation. The drier season lasts 6.5 months, from April 1 to October 17. The month with the fewest wet days at Pretoria is July, with an average of 0.4 days with at least 0.04 inches of precipitation. Among wet days, we distinguish between those that experience rain alone, snow alone, or a mixture of the two. The month with the most days of rain alone at Pretoria is December, with an average of 15.6 days. Based on this categorization, the most common form of precipitation throughout the year is rain alone, with a peak probability of 52% on December 18. 5 Rainfall To show variation within the months and not just the monthly totals, we show the rainfall accumulated over a sliding 31-day period centered around each day of the year. Pretoria experiences significant seasonal variation in monthly rainfall. The rainy period of the year lasts for 8.1 months, from September 9 to May 11, with a sliding 31-day rainfall of at least 0.5 inches. The month with the most rain at Pretoria is January, with an average rainfall of 3.8 inches. The rainless period of the year lasts for 3.9 months, from May 11 to September 9. The month with the least rain at Pretoria is July, with an average rainfall of 0.1 inches. TOPOGRAPHY OF THE PROPOSED AREA For the purposes of this report, the geographical coordinates of Pretoria are -25.733 deg latitude, 28.183 deg longitude, and 4,327 ft elevation. The topography within 2 miles of Pretoria contains significant variations in elevation, with a maximum elevation change of 574 feet and an average elevation above sea level of 4,284 feet. Within 10 miles contains significant variations in elevation (1,342 feet). Within 50 miles contains very significant variations in elevation (2,927 feet). The area 6 within 2 miles of Pretoria is covered by artificial surfaces (100%), within 10 miles by artificial surfaces (69%) and grassland (13%), and within 50 miles by grassland (34%) and cropland (26%). The most elevated portion of the area is situated along its southern boundary. The country displays a gradual regional slope to the north, the continuity of which is locally broken by hills and ridges of resistant rocks such as the chert bands in the upper Dolomite Series and the quartzite bands of the Pretoria Series. Prominent quartzite ridges are the Magaliesberg and Witwatersberg. The southern portion of the area approaches the Highveld in its characteristics, and forms undulating to hilly country. The western, central and eastern portions largely fall in the Middleveld and are also called "Bankeveld". This is characterized by roughly parallel hills, ridges and escarpments with longitudinal valleys between. The northern portion forms part of the Bushveld, which in this area is occupied by comparatively flat to undulating country, the monotony of which is relieved by ridges of granophyre and gabbro. The "Pyramid" line of hills increases in height above the surrounding flats from east to west, i.e. from 120 m at Bon Accord to 300 m at Kareepoortberg. VEGETATION The landscape is highly variable, with extensive sloping plains and a series of ridges slightly elevated over undulating surrounding plains. The vegetation is species-rich, wiry, sour grassland alternating with low, sour shrubland on rocky outcrops and steeper slopes. Most common grasses on the plains belong to the genera Themeda, Eragrostis, Heteropogon and Elionurus. A high diversity of herbs, many of which belong to the Asteraceae, is also a typical feature. Rocky hills and ridges carry sparse (savannoid) woodlands with Protea caffra subsp. caffra, P. welwitschii, Acacia caffra and Celtis africana, accompanied by a rich suite of shrubs among which the genus Searsia (especially S. magalismonata) is prominent. FIELD AND LAB WORK PROPOSAL Field testing is done at the project site. Certified professionals carry out field testing services for various construction projects that can include roadways, bridges, utility projects, airports, and building developments. Typically, soil sampling is a method of removing sub-surface earth materials. These soil samples can be evaluated in the field or taken back to the lab for further testing. The technicians check for moisture and compaction, which will affect the building's foundation. It seems obvious, but it is critical to have a strong foundation, without issues, before construction begins. This includes the ground to be built upon and the materials used to build the structure. Material testing ensures that the project will be successful before the foundation is laid. Without this testing, builders and engineers will not be aware of the quality of the sub-surface and materials and whether they will meet the project's requirements. Other types of field testing include: Soil and Aggregate Sampling and Testing Compaction and Density Bearing Ratio Permeability Testing Lab testing is when material samples are taken back to an off-site location or lab to review and analyze. Don't confuse this with product testing, which is also done in a lab and involves reviewing, testing, and providing reports on finished products, such as doors, windows, curtainwalls, and roofing products. Pre-testing finished products and how they perform in a lab does not guarantee how well they will perform in the field, especially if the construction materials that support the finished products have 7 not been properly tested and inspected. Lab testing on material samples such as soil, asphalt, aggregate, concrete, and masonry taken from the field site is a reliable method to provide detailed analysis on the materials, ensuring that the materials on a job site will not cause any project-related issues. Lab tests can also be performed if the field testing results prove inconclusive or a more detailed analysis is needed. Unconfined Compression Test on Rock The unconfined compression test is the type of laboratory test that is used to determine the strength of rocks. Unconfirmed compressive strength of rocks may be defined as the maximum axial compressive stress that the specimen can withstand under zero confining stress. This test is used extensively in geotechnical designs and construction. Triaxial Compression Test on Rock Triaxial Compression Test may be defined as the type of compression test in which the cylindrical rock specimen is encased in an impervious membrane and is subjected to a confining pressure and finally loaded axially to failure. It is very similar to the triaxial compression test carried out on the soil. Since the test procedure involves the application of lateral pressure and deviator stress thus a special type of equipment is necessary for encompassing the large stresses. In general, the specimen of rock is first subjected to confining pressure then gradually the deviatoric stress is applied to keep the confining pressure constant. The specimen is usually enclosed in a jacket that is made up of polyurethane which is oil resistant. Ultrasonic Testing Is used to determine the pulse velocities of compression and shear waves in intact rock and the ultrasonic elastic constants of isotropic rock. Ultrasound waves are transmitted through a carefully prepared rock specimen. The ultrasonic elastic constants are calculated from the measured travel time and distance of compression and shear waves in a rock specimen. The ultrasonic evaluation of elastic rock properties of intact specimens is useful for rock classification purposes and the evaluation of static and dynamic properties at small strains (shear strains < 10-4 %). Older equipment only provides ultrasonic P-waves measurements, while new designs obtain both P- and S-wave velocites. When compared with wave velocities obtained from field geophysical tests, the ultrasonics results provide an index of the degree of fissuring within the rock mass. This test is relatively inexpensive to perform and is nondestructive, thus may be conducted prior to strength testing of intact cores to optimize data collection ASSUMPTIONS AND LIMITATIONS Even though every care is taken to ensure the accuracy of this report, environmental assessment studies are limited in scope, time and budget and therefore largely subjective. Discussions and proposed mitigations are to some extent made on reasonable and informed assumptions, built on bone fide information sources, and deductive reasoning and personal experience. The interpretation of the overall geotechnical conditions along the powerline route is based upon a review of available information on the project area. Subsurface and geotechnical conditions have been inferred at a desktop level from available information, past experience in the project area and professional judgement. The information and interpretations are given as a guideline only and there is no guarantee that the information given is totally representative of the entire area in every respect. 8 OHS REQUIREMENTS The Site Investigation Code of Practice establishes a standard of "acceptable engineering practice" to assist the construction industry (client, project manager, consultant, contractor) in the planning, design and execution of geotechnical site investigations in southern Africa. the following legislation should be considered: Mine Health and Safety Act, No. 29 of 1996. National Water Act, No. 36 of 1998. Occupational Health and Safety Act, No 85 of 1993. Housing Consumers Protection Measures Act, No. 95 of 1998. National Building Regulations and Building Standards Act, No. 103 of 1977. Natural Scientific Professions Act, No. 106 of 1993. Engineering Professions Act, No. 114 of 1990. Minerals Act, No. 50 of 1991. STOME WATER DRAINAGE CONCEPTS All the main streams flow to the north in conformity with the general "lope. They are the Crocodile, Magalies, Jukskei, Hennops, Apies and I'ienaars Rivers and their tributaries. The main streams and some of their tributaries are frequently undeflected in their courses by prominent ridges and locally they have incised steep gorges or valleys in the resistant beds at right angles or oblique to the strike. Some of the gaps in the ridges have been predetermined by faults, for instance on Zwavelpoort 373 JR, Tiegerpoort 371 JR and at Hartbeespoort Dam, but most of the steep valleys formed by the Crocodile, Hennops and Skeerpoort Rivers bear no relationship to pre-existing faults. The drainage has evidently been predetermined by the erosion pattern of the Karoo beds prior to denudation; in other words, the drainage is superimposed on the pre-Karoo structures. Subsequent younger drainage by longitudinal streams on less resistant shaly beds has given rise to the formation of broad valleys between the ridges. Resequent tributaries have incised the dip slopes on the northern side of the ridges, and the steeper slopes to escarpments on the southern side. Some of these streams have cut across the crest line and smaller catchment areas have been formed on the other side. The erosional power of these streams is evidently not caused by the supply of water from the catchment areas, but by cutting and lowering of their base levels. A more advanced stage is displayed by the Skeerpoort River and the upper course of the Magalies River, which during the process of back cutting have reached the dolomite. Sources of underground water in the dolomite were tapped, which increased the erosional power of the streams and their tributaries. Stream capture may also have played a role; for instance the former course of the Magalies River probably more or less coincided with the Swartspruit, whereas its present course may have been originally a tributary, which cut backward on Zeekoehoek 509 JQ and Doornbosch 508 JQ until it captured the upper course of the Swartspruit north of Magaliesburg. Rejuvenation of the entire stream pattern and a general lowering of the main base levels probably took place during uplift of the continent in late post-Karoo times. The formation of local base levels is rather exceptional, but well illustrated by the Hennops River. The gradient of the latter between Wierda Bridge and the upper chert zone in the dolomite is 1:277 and between the chert zone and the Crocodile River 1:181. The gradients of the Swartbooispruit and Rietspruit, however, decrease downstream in a normal way_ UNDERGROUND WATER RESOURCES Pretoria owes its initial development to the so-called IIfountains" or springs that rise in the dolomite south of the city. Even today about 20% of the city's water requirements of some 200 000 mJjday are 9 obtained from dolomite springs in the Fountains, Kafferspruit and Sterkspruit valleys. The rest is supplied by the Rand Water Board from the Vaal River catchment on the other side of the continental divide. Because of the duplication of outcrops by a strike overthrust there are two bodies of dolomite south of Pretoria separated by rocks of the Pretoria Series. The lowest part of the outcrop of the eastern body of dolomite lies in the Kafferspruit valley upstream of the Rietvlei Dam and there groundwater overflows from the dolomite at several widely separated springs. The exact position of each spring is probably determined by the disposition of the various dykes that occur there in relation to the topographical relief. The western body of dolomite is divided by the Pretoria dyke into an eastern and a western part and, as this dyke is the locus of the deep ,Fountains valley drained by the headwater of the Apies River, the lowest points of the outcrops of both parts of the dolomite are on either side of the Pretoria dyke in this valley as indicated by the geological map after Cilliers (1953), figure 5. Overflow of groundwater from the eastern part of the western dolomite body at the Sterkfontein springs near Olifantsfontein also contributes to the Pretoria city's supply. Available data on groundwater in the Pretoria area are presently (1975) being assembled and processed (and will form the subject of a proposed separate Geological Survey publication). GEOLOGY OF THE AREA The Donkerhoek batholith comprises mainly metaluminous to strongly peraluminous granites. Numerous late-tectonic dykes, pegmatites, and aplites occur also (Clemens et al. 2017; Miller 2008). The Donkerhoek batholith also includes minor volumes of magnesian, metaluminous to peraluminous calc-alkaline rocks, such as quartz diorites, monzogranites, granodiorite, and tonalite (Clemens et al. 2017; McDermott et al. 1996). The Kurikaub granodiorites and tonalites and the Nomatsaus granites are part of this suite. Exposures of the rock types are generally in the form of few isolated small-scale domes and flat-lying outcrops near river banks. Textures of the Nomatsaus granite are equigranular with generally no preferred orientation of the rock-forming minerals. Although outcrop evidence is restricted to small-scale domes at the river bank, the intrusion appears structureless. Enclaves are absent. The host rocks of the Nomatsaus intrusion are other granites of the Donkerhoek batholith, however, due to coverage of the area with gravel and sometimes grass beds contacts are not exposed. PROBLEM SOILS IN THE AREA Field observation and laboratory test can be useful to identify problematic soils. Some properties of soils such as dry density and liquid limit are helpful to estimate collapsibility potential of soils. In this regard, it was done a series laboratory tests to evaluate the collapsibility rate. Problem soils can be naturally occurring or man-made soils. This includes soils that have been displaced naturally or by man. Problem soils can give rise to many geotechnical difficulties including inadequate bearing capacity, the potential for unacceptable settlements and slope instability. There are many types of problem soils, some of the most noteworthy being expansive soils, collapsible soils, soft clays and dispersive soils. Most of the damage to structures in South Africa is related to soil characteristics, with expansive and collapsing soils causing the most problems. In addition to the well documented historic concerns dealing with specific problem soils, recent encounters with significant situations have highlighted the need for a comprehensive documentation on the role of remote sensing and GIS technologies for mapping, characterizing and monitoring problem soils in South Africa. In Gauteng, but more specifically in Tshwane, the primary causes of sinkholes are concentrated stormwater ingress, especially after heavy rains, or leaking water-bearing infrastructure. Decline of water levels drought, groundwater pumping (wells, quarries, mines) Disturbance of the soil - digging through soil layers, soil removal, drilling. Point-source of water - leaking water/sewer pipes, injection of water. Colluvium and Alluvium 10 Colluvium is an all-embracing term that includes all soils on hill or mountain slopes that have moved down-slope under the influence of gravity and un-concentrated surface wash. Coarse colluvium includes talus, slide debris and colluvial gravel whilst fine grained hill wash consists of clayey or silty composition with variable amounts of sand. Slope instability is the main concern on talus slopes whilst silty or clayey hill wash exhibit potential expansive characteristics with soil moisture fluctuations or might be potentially collapsible and compressible when subject to load. Alluvial deposits result from the transportation and deposition of sediment by rivers. Within the channel sediment accumulations are of limited areal extent and include transitory bedload deposits and alluvial islands, formed initially of coarse sediment and subsequently overlain by finer material. Along the margins of channels there are lateral deposits in the form of discontinuous bars in straight channels, or point bars on the convex of meanders. Accumulations of sediment in aggrading or abandoned channels are termed channel fills. ENVIRONMENTAL CONSIDERATIONS Environmental considerations include strategies, development guidelines and land use plans related to greenspaces, derelict and contaminated land, nature conservation and biodiversity, flooding, air and water quality, green design and climate change. The impact of the development from a geotechnical perspective will be restricted to the removal and displacement of soil, boulders and bedrock referred to in this report as “subsoils”. The levelling of areas to create building platforms will also result in the displacement and exposure of subsoils. These impacts will have a negative visual impact on the environment, which in some cases can be remediated. The project requires extensive earthworks to meet the required horizontal and vertical alignments and curvatures for roads, so the aesthetic impact is significant. Every stage of any construction project has a measurable impact on the environment: the use of raw materials, transportation of materials from source to the building site, the environmental footprint of the construction site, use of water, as well as waste removal and disposal. Trees and other plants near the wires have to be maintained to keep them from touching the wires. On some power line corridors, herbicides are used to control vegetation. When power lines and their access roads are placed in undeveloped areas, they can disturb forests, wetlands, and other natural areas. Emissions of greenhouse gases and other air pollutants, especially when a fuel is burned. Use of water resources to produce steam, provide cooling, and serve other functions. Discharges of pollution into water bodies, including thermal pollution (water that is hotter than the original temperature of the water body). RECOMMENDATIONS AND CONCLUSION The project is moderately complex due to three alternatives and all have the same geotechnical constraints as there are no changes in the geology. The geotechnical constraints can only be verified and described in detail after the fieldwork phase, i.e. excavation of test pits etc. It is recommended that a detail geotechnical investigation be conducted along the power line routes as well as substation site in order to verify this desk study and to provide site specific appropriate founding solutions. The recurrence interval of mining induced seismic events and potential undermining should be determined and taken into consideration for the design of pylons and the substation. 11 REFERENCES Diop, S., Stapelberg, F., Tegegn K., Ngubelanga, S. & Heath, L. 2011. A review of problem soils in South Africa. Council for Geoscience Report Number: 2011-0062. Guidelines for Urban Engineering Geological Investigations 1995. Published by SAIEG & SAICE. National Home Builders Registration Council (NHBRC). Home Building Manual, part 1 & 2, first 12