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ROSINVEST (Z) LIMITED
ENVIRONMENTAL IMPACT STATEMENT (EIS)
FOR THE PROPOSED TIN MINING IN CHIROBI
VILLAGE OF MAPATIZYA CONSTITUENCY OF
KALOMO DISTRICT SOUTHERN
PROVINCE OF ZAMBIA
UNDER LARGE MINING LICENSE
NO. 16395-HQ-LPL
DEVELOPER:
ROSINVEST ZAMBIA LIMITED,
PLOT 66B CENTRAL STREET,
JESMONDINE,
LUSAKA, ZAMBIA.
CELL: 0977 808008
EMAIL: info@rosinvest.co.zm
CONSULTANTS:
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
SUITE F11 GREAT NORTH MALL,
GREAT NORTH ROAD,
LUSAKA, ZAMBIA.
CELL: 0977 864057
EMAIL: tropicalenvironmental123@yahoo.com
ENVIRONMENTAL IMPACT STATEMENT (EIS)
SEPTEMBER 2014
AF
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FIRMATION
Rosinvest Zambia Limited hereby affirms that the information presented in this report reflects
our environmental management commitments. Therefore, necessary resources shall be made
available by our management to fulfill our commitments as presented in this report. We also
acknowledge that failure to implement our commitments and any approval conditions that may
be issued by the Zambia Environmental Management Agency (ZEMA) will be contrary to
environmental and social laws in Zambia.
Name: Mr. Edward Simukonda
Signature: ………………………………….
Date: 12th June 2014
Mine Manager/Holder
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EXECUTIVE SUMMARY
This Environmental Impact Statement (EIS) have been prepared by Tropical Environmental
Management Experts (TEME Consultants) for Rosinvest Zambia Limited (Developer) a Private
Joint Venture Company between Daled Mining Limited and Vidayu Holdings Corporation
Zambia Limited.
Rosinvest Zambia Limited is a Private Joint Venture company between Daled Mining Limited
and Vidayu Holdings Corporation Zambia Limited who has acquired a Tin Mining Area in
Chirobi Village of Kalomo District Southern Province of Zambia. The company was registered
by the government of Zambia as a Private Limited Company on the 26th day of February, 2014
with the Company Registration No. 120174 and it is currently holding a Large Tin Mining
License under Daled Mining Limited in Mapatizya Constituency of Kalomo District.
The mine for which this Environmental Impact Statement (EIS) report is prepared for is located
in Chiefdom Simwata Chela of Chirobi village, Mapatizya Constituency of Kalomo District on a
Large Mining License No. 16395–HQ–LPL. The mine approximately covers an area of about
40km2. It is about 165Km from Mapatizya Junction off Great North Road (T2).
The project under consideration involves open pit mining of Tin, Transportation of Overburden
Material to the Overburden Dump, Dewatering the Open Pit, Servicing of Equipment, Hand
Picking of Tin if seen in the Pit and Transportation of the Tin Ore to the Crushing and Smelter
Plant. Support facilities include a Mine Camp for 82 workers, Security Fence, Explosives
Magazine, Generator, settling Pond for Dewatering Water, Hired Earth Moving Machines, Water
Bowser, Fuel Bowser, Service Workshop, Borehole and an Administration Office support the
above.
The lifespan of the Mine has been estimated at 40 years with a possibility of extension if
exploration is carried out and more tin resources are discovered.
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Some of the Key and relevant legislation to this proposed project are the Environmental
Management Act No. 12 of 2011 and its regulations, the Mines and Minerals Development Act
No. 7 of 2008 and its regulations. Legislation on the workers welfare is also relevant to this
proposed project. All relevant legislation that is key and relevant to this proposed developmental
project has been discussed under the legal and policy framework chapter of this EIS report.
Post mine acquisition activities (mainly for maintenance reasons) included installation of a
security fence, accommodation containers, continuation of dewatering activities, stabilizing the
open pit and general housekeeping activities.
PROJECT ENVIRONMENT
The proposed mine is approximately 4 hectares in extent. The terrain is high and flat. The main
vegetation cover is natural vegetative canopy of medium density with occasional ridges and hills
hidden beyond the canopy. Most of the vegetation in the project site has not been affected by
anthropogenic activities because for a long period access to the area by local people has been
restricted. Vegetation covers within the proposed project site are Brachystegia allenii (mutondo)
woodland with Muombo woodland, moderate grass covers in the slopes, Pterocarpus angolensis
(mulombwa). The extraction of the Tin from Cassiterite will revert the site to above level visual
access in the area except for the vegetative canopy crowning the forest with its nature beauty.
SCOPING AND CONSULTATIONS
A scoping process was conducted to identify and determine potential impacts of significance that
would form the basis of the study and to eliminate issues unlikely to be of importance. In order
to take into account public views in this process, a public consultation meeting regarding the
proposed project and EIA study was held on 13th March 2014 and attended by different
stakeholders. The results of this meeting together with deliberations within the study team
formed a basis for determining the project Terms of References (TORs). Consultation with
government institutions, local authorities and relevant stakeholders and interested and affected
parties had continued throughout the study process as found necessary.
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The scope of the study follows the EIA terms of reference for review. It consisted of three main
phases, firstly the preliminary actions and scoping exercise; secondly the baseline studies and
data collection; impacts and their mitigation measures. The study addresses issues surrounding
the following aspects of the environment;
Land and soil;
Air quality and noise environment;
Surface water;
Underground water and quality;
Occupational health and safety;
Public health and safety;
Traffic, road safety and public access;
Local Ecosystem, vegetation and habitat; Land use/ Aesthetics;
Employment and multiplier effects
POTENTIAL SOCIO AND ENVIRONMENTAL IMPACTS
Positive impacts of the project include a significant contribution to Large Scale Mining
development in Zambia and provision of job opportunities to the local Kalomo/Chirobi
Residents. Other benefits include tax to government, revenue contribution to the local authority,
local business opportunity development and profit to the company for further investment in large
scale mining development.
Just like other mining related projects, negative impacts of the project for which mitigation
measures have been proposed are summarized below in the order of significance.
Social challenges for employees due to the camping arrangement which makes them
leave their families during all the working days of the week: - Mitigation measures for
this impact include ensuring that employees go home during weekends and they are
entitled to annual leave. Counseling services shall also be provided to all employees and
their families.
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Conflicts with the community and nearby mines: - This impact shall be managed by
continuing with stakeholder engagement and putting in place a grievance management
system which shall be publicized to the community once developed none of the residents
will be removed from their settlements because the mining activities will be more than
5km away from any human settlements.
HIV/AIDS related challenges due to limited time at home by employees and by
having more money in their pockets: - This shall be managed through professional
counseling services and support for employees living with HIV/AIDS.
Occupational health and safety problems due to exposure of employees to dust,
hazardous waste and explosives: - Various operating procedures have been proposed
and these include provision of protective clothes, monitoring and annual medical checkups for all the employees.
Air pollution due to release of dust from the open pit, from the overburden dump,
from roads and from open spaces within the camp: - This shall be managed by
frequent dust suppression using a water bowser and monthly ambient dust monitoring
which shall include monitoring dust in confined working places.
Water pollution due to dewatering activities, effluent from the machinery washing
bay, effluent from the workshop and due to sewage disposal: - Water from the pit
shall be pumped into a settling pond for settling off solids before discharge, all the
effluent from the washing bay and the workshop shall be directed into an oil/water
separator before discharge and a modular sewage treatment plant has been proposed for
treatment of sewage.
Noise and vibration due to blasting and movement of machinery: - Noise monitoring
shall be done frequently, noise protective clothes shall be provided to workers and
warning signs to show places where protective clothes are required shall be installed.
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Loss of flora and fauna due to site clearing activities: - This shall be management by
restricting site clearing to specific areas, routine security patrols of the mine licensed
area, prohibiting charcoal burning, obtaining a site clearing permit from management
before site clearing and conducting conservation awareness activities.
Landscape change and land degradation due to mining and overburden disposal: This shall be managed by re-vegetation of the overburden dump and minimizing site
clearing. Rehabilitation of contaminated sites in the entire mine area shall also be
conducted.
ENVIRONMENTAL MANAGEMENT AND MONITORING
To implement all the commitments herein, an environmental management and monitoring plan
has been proposed. Major issues that shall be monitored frequently include air quality, water
quality, flora and fauna, soil quality, climate, waste management and socio-economic issues.
MANAGING DIRECTOR STATEMENT
I, Mr. Edward Simukonda Project Manager for Rosinvest on behalf of the Director, declare
that the information presented in this report is nothing else but only the truth about Rosinvest‟s
intention regarding the proposed project.
Signature: ___________________________
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C O N T E N T S
1.0
INTRODUCTION
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1.1
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BACKGROUND OVERVIEW
1.2
1.3
1.4
1.5
2.0
3.0
SCOPE OF WORK
OBJECTIVES
THE COMPANY/CONTACT DETAILS
TRACK RECORD/PREVIOUS EXPERIENCE OF THE PROJECT
DEVELOPER
1.6
COMMENCEMENT OF THE PROJECT
1.7
THE EIA STUDY
1.8
SCOPE OF THE EIA STUDY
1.9
METHODOLOGY
1.9.1 PHASE 1: PRELIMINARY ACTIONS AND SCOPING
1.9.2 PHASE 2: BASELINE STUDY AND DATA COLLECTION
1.9.3 PHASE 3: IMPACT ASSESSMENT AND RECOMMENDATION
LEGAL AND POLICY FRAMEWORK
2.1
BRIEF HISTORICAL BACKGROUND OF THE LEGAL AND POLICY
FRAMEWORK IN ZAMBIA
2.2
THE ENVIRONMENTAL MANAGEMENT ACT NO. 12 of 2011
2.3
THE MINES AND MINERALS DEVELOPMENT ACT NO. 7 of 2008
2.4
THE OCCUPATIONAL HEALTH AND SAFETY ACT NO. 36 OF 2010
2.5
THE PNEUMOCONIOSIS ACT NO. 13 OF 1994
2.6
THE NATIONAL HERITAGE CONSERVATION COMMISSION ACT
2.7
THE ROAD TRAFFIC ACT
2.8
THE FOREST ACT CAP199 OF 1973
2.9
THE ZAMBIA WILDLIFE ACT, NO. 12 OF 1998
2.10
THE FISHERIES ACT OF 1974
2.11
THE PETROLEUM ACT CAP 439 AND THE ENERGY REGULATION
ACT CAP 436
2.12
TOWN AND COUNTRY PLANNING ACT CAP 475 OF 1962
2.13
THE LOCAL GOVERNMENT ACT OF 1991
2.14
PUBLIC HEALTH ACT CAP 295 OF 1978
2.15
LANDS ACT CAP 29 OF 1995
2.16
EMPLOYMENT ACT CAP 268
2.17
THE WATER SUPPLY AND SANITATION ACT NO. 28 OF 1997
2.18
THE WATER ACT, CAP 312 OF 1948
2.19
MINIMUM WAGES AND CONDITIONS OF EMPLOYMENT
ACT (CAP 276)
2.20
WORKERS COMPENSATION ACT No. 10 OF 1999
2.21
INTERNATIONAL CONVENTIONS AND PROTOCOLS
BASALINE DESCRIPTION OF THE ENVIRONMENT
3.1
BIO-PHYSICAL ENVIRONMENT AND GEO-ENVIRO
3.1.1 DESCRIPTION AND LOCATION OF THE SITE
3.1.2
ECOLOGY
3.1.3 CLIMATE
3.1.4
HYDROLOGY
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3.1.5 GEOLOGY AND GEOMORPHOLOGY
3.1.6 TOPOGRAPHY
3.1.7 LANDSCAPE
3.1.8 SOILS
3.1.8 FLORA
3.1.9 FAUNA
3.2. SOCIO- ECONOMIC AND CULTURAL ENVIRONMENT
3.2.1 DISTRICT BACKGROUND
3.2.2 GOVERNMENT, ADMINISTRATION AND POPULATION
CHARACTERISTICS
3.2.3 HEALTH/INFRASTRUCTURES
3.2.4 EDUCATION/INFRASTRUCTURES
3.2.5 TRANSPORT TRADE AND COMMUNICATION
3.2.6 LAND USE IN THE PROJECT AREA.
3.2.7 LAND OWNERSHIP AND LAND TENURE
3.2.8 WATER AND SANITATION
3.2.9 EMPLOYMENT CREATION
3.2.10 ARCHAEOLOGICAL SITE
3.2.11 SOCIAL-CULTURAL
PROJECT DESCRIPTION
4.1
BACKGROUND, OBJECTIVES AND NATURE OF THE PROJECT
4.1.1 BACKGROUND OVERVIEW
4.1.2 OBJECTIVE OF THE PROJECT
4.1.3
COMPONENTS OF THE PROJECT
4.1.4 NATURE OF THE PROJECT
4.1.4.1 OPEN PIT MINING PROCESS AND MINING
MACHINERY
4.1.4.2 MINING DESIGN
4.1.4. 3 OVERBURDEN DUMP (OB)
4.1.4.4 ORE CRUSHING, WASHING PLANT,
CONCERTRATOR AND SMELTER
4.1.4.4.1 CONCENTRATOR DESIGN
4.1.4.3.2 SMELTER DESIGN
4.1.4.5 DOMESTIC WASTE AND SEWAGE
MANAGEMENT
4.1.4.6
DE-WATERING, DOMESTIC WATER AND WASTE
WATER FACILITIES
4.1.4.7 FUEL STORAGE FACILITIES
4.1.4.8 MINE SITE ACCESS ROAD
4.1.4.9 ACCOMMODATION AND SECURITY FACILITIES
4.1.4.10 MECHANICAL AND METAL FABRICATION
WORKSHOP
4.1.4.11 SALVAGE YARD
4.1.4.12 EXPLOSIVES STORAGE FACILITIES
4.1.4.13 DUST SUPPRESSION FACILITIES
4.1.4.14 HEAVY MACHINES AND LIGHT VEHICLE
WASHING BAY
4.2
DESCRIPTION OF THE PROJECT LIFECYCLE ACTIVITIES
4.3
PROJECT INPUTS AND OUTPUTS
PROJECT ALTERNATIVES
5.1
NO PROJECT, AVOID OR POSTPONE ALTERNATIVE
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5.3
5.4
5.5
6.0
7.0
8.0
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SITE ALTERNATIVES
MINING METHODS
ORE PROCESSING
HIRING OF MINING MACHINES AGAINST BUYING THE
MACHINES
5.6
MINING WASTE DISPOSAL ALTERNATIVES
5.7
CONSTRUCTION OF THE WASHING PLANT AND CRUSHER
5.8
POWER SUPPLY ALTERNATIVES
5.9
FUEL STORAGE ALTERNATIVES
5.10
DOMESTIC WASTE DISPOSAL FACILITIES
5.11
SEWAGE MANAGEMENT
5.12
“WITHOUT PROJECT” ALTERNATIVE”
5.13
PROCESS AND MATERIALS
ENVIRONMENTAL IMPACT ANALYSIS AND MITIGATION
MEASURES
6.1
OBJECTIVE
6.2
LEGISLATION, COMPANY POLICIES AND LIMITATIONS
6.3
PRE-MINING PHASE IMPACTS AND MITIGATIONS
6.3.1 Introduction
6.3.2 Summary of the Environmental Impacts – Pre-Mining Phase
6.3.3 Pre-Mining Impacts Mitigation and Management
6.4
OPERATIONAL PHASE ENVIRONMENTAL IMPACTS
AND MITIGATIONS
6.4.1 Introduction
6.4.2 Environmental Impacts – Mining (Operational) Phase
6.5
SOCIAL IMPACT ASSESSMENT
6.5.1 Introduction
6.5.2 Impacts and Mitigations Measures
6.6
IMPACT EVALUATION CRITERIA
6.6.1 NATURE OF IMPACT
6.6.2 DIRECT IMPACT
6.6.3 INDIRECT IMPACT
6.6.4SPATIAL EXTENT
6.6.5 FREQUENCY
6.6.6 DURATION
6.6.7INTENSITY
6.6.8 SEVERITY
6.6.9 PROBABILITY
6.6.10 SENSITIVITY
6.6.11 DETERMINATION OF SIGNIFICANCE
ENVIRONMENTAL MANAGEMENT AND MONITORING PLAN
7.1
INSTITUTIONAL FRAMEWORK FOR MONITORING, REPORTING AND
SUPERVISION
7.1.1 MONITORING ARRANGEMENTS
7.1.2 OPERATIONAL PHASE
CLOSURE AND DECOMMISSIONING
8.1
GENERAL APPROACH
8.2
RECLAMATION ACTIVITIES
8.2.1 TOPSOIL SALVAGE
8.2.2 GRADING DISTURBED AREAS
8.2.3 REVEGETATION
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8.3
9.0
CLOSURE AND DECOMMISSIONING OF MINE COMPONENTS
8.3.1 OPEN PIT
8.3.2 WASTE ROCK DISPOSAL FACILITY
8.3.3 ORE STOCKPILE
8.3.4 PLANT SITE
8.3.5 TAILINGS STORAGE FACILITY
8.3.6 WATER STORAGE FACILITY
8.3.7 SEDIMENT CONTROL STRUCTURES
8.3.8 ROADS
8.3.9 ANCILLARY FACILITIES
8.4
MONITORING
CONCLUSION AND RECOMMENDATIONS
9.1
FINDINGS OF THE EIA
9.2
RECOMMENDATIONS
9.3
CONCLUSION
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ABBREVIATIONS AND ACRONOMYNS
dBA
Decibels on the “A” Scale
CBD
Convention on Biological Diversity
EIA
Environmental Impact Assessment
EIS
Environmental Impact Statement
EMP
Environmental Management Plan
EMMP
Environmental Management and Monitoring Plan
EMA
Environmental Management Act
FNDP
Fifth National Development Plan
GDP
Gross Domestic Product
HIV/AIDs
Acquired Immune Deficiency Syndrome
Km
Kilometer
Kph
Kilometers per hour
MMDA
Mines and Minerals Development Act
MSD
Mine Safety Department
NAPSA
National Pension Scheme Authority
NCS
National Conservation Strategy
NEAP
National Environmental Action Plan
NHCC
National Heritage Conservation Commission
OB
Overburden
PAYE
Pay As You Earn
PMT
Project Management Team
SI
Statutory Instrument
STDs
Sexually Transmitted Diseases
TORs
Terms of Reference
USD
United States Dollar
VAT
Value Added Tax
(Z)
Zambia
ZABS
Zambia Bureau of Standards
ZEMA
Zambia Environmental Management Agency
ZRA
Zambia Revenue Authority
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LIST OF TABLES
Table 1
Particulars of Shareholders
20
Table 2
Details of Directors
20
Table 3
Chemical analysis results
47
Table 4
Species of Area;
51
Table 5
Animal Species
54
Table 6
Population of Kalomo District (CSO Preliminary Report of 2010)
56
Table 7
Project Inputs and Outputs
80
Table 8
Environmental Impacts Pre-Mining Phase
90
Table 9
Air Pollution
108
Table 10
Water and Soil Pollution
109
Table 11
Noise and Vibration
111
Table 12
Loss of Flora and Fauna
112
Table 13
Non-Hazardous and Hazardous Waste Generation
113
Table 14
Occupational Health and Safety
114
Table 15
Social Challenges by Employees
115
Table 16
Conflicts with the Local Community and Nearby Mines
117
Table 17
HIV/AIDS Related Challenges
118
Table 18
Disease Vector
119
Table 19
Evaluation of Impacts
150
Table 20
Environmental Management and Monitoring Plan (EMMP)
154
Table 21
Monitoring and Reporting Responsibilities
162
Table 22
Decommissioning and Closure Activities and Cost Estimates
173
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LIST OF ANNEXTURES
I.
II.
ATTENDANCE REGISTER
MINUTES OF THE MEETING
III.
LETTER FOR THE TERMS OF REFERENCES
IV.
CVs OF THE EIA TEAM
V.
VI.
VII.
VIII.
IX.
X.
XI.
XII.
MINING LICENSE
DALED CERTIFIECATE OF INCEORPORATION
ROSINVEST CERTIFICATE OF INCORPORATION
MINE LAYOUT
CONCENTRATOR DESIGN
SMELTER DESIGN
CRUSH PLANT
TIN ORE PROCESSING PLANT
XIII.
STONE PRODUCTION LINE
XIV.
GRAVITY CONCERNTRATOR CIRCUIT
XV.
XVI.
XVII.
XVIII.
XIX.
XX.
XXI.
ROCK CRUSHING CIRCUIT
TANK DESIGN
UNZA LABORATORY RESULTS
LETTER FROM THE CHIEF
SITE LOCATION MAP
TOPOGRAPHICAL MAP
GEOLOGICAL MAP
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1.0
ROSINVEST -EIS
INTRODUCTION
1.1
BACKGROUND OVERVIEW
Mineral resources of the nation reflect in terms of potential economic growth of the country at
large. Our natural mineral wealth has been exploited considerably during the past years. With
increase in industrialization coupled with population growth, the demand for different minerals
has increased and is likely to grow further in years to come. With liberalized mining sector, there
are efforts by locals and foreigners to take a share in the mining industry. Most investors have
since ventured into mining at both small and as well large scale.
The Tin Belt of the Southern Province of Zambia has a history of small working extending over
Sixty years, with limited production from numerous small eluvia, alluvial and pegmatite
deposits, co-operative tin mining was initiated in 1963, but ceased in 1965 following Rhodesia‟s
unilateral declaration of independence. The Geological Survey Department carried out a study of
all known occurrences in 1967 and 1968 in order to assess the potential of the area as a
preliminary to re-activating co-operative mining. (See expanded Geological Maps in Annex 21).
Fig 1: Tin Belt of Southern Province
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Fig 2: Geological Map of Zambia
Zambia is an attractive investment destination offering various lucrative investment
opportunities in mining tourism, agriculture, manufacturing, energy. The investment climate is
characterized by a stable macroeconomic environment, stable political system, investment
guarantees and security.
Rosinvest Zambia Limited is one such Company which has been attracted by the aforesaid
incentives. To break through the market, the company would like to invest in the Tin Mining
project in Chiefdom Simwata Chela of Chirobi Village, Kalomo District of the Southern
province of Zambia.
The company plans to spend US$6,508,000 (Six million Five Hundred Eight Thousand
dollars) to implement and start its operations of the project. The life of mining is estimated about
40 years, tin average cost of producing tin ingot at the site is estimated at USD 4500 per ton.
This includes costs for mining, concentrating, smelting, and government taxes.
The project site is located in Chiefdom Simwata Chela of Chirobi village, Mapatizya
Constituency of Kalomo District on a Large Mining License No. 16395 – HQ – LPL. The site is
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about 165Km from Mapatizya Junction off Lusaka Livingstone Road (T2) and is approximately
about 40km2.
1.2
SCOPE OF WORK
The Project falls under the Environmental Management Act (EMA) No.12 of 2011 of the
Environmental Impact Assessment (EIA) Regulations and it is therefore a requirement that an
Environmental Impact Assessment (EIA) study is carried out for the project. The Environmental
Impact Statement (EIS) presents the findings of the study to identify both positive and negative
impacts together with recommendations to mitigate potential negative impacts and to enhance
benefits.
The scope of work for this report includes identifying all the key project aspects (activities that
interact with the environment) and proposing management measures as a means of mitigating
environmental impacts. Major components of the report therefore include the project description,
environmental impact analysis, mitigation measures and a Decommissioning and Closure Plan.
The scope of work for the Project baseline study included:
A desk study of all available information on the project area;
Visits to government departments, Non-Governmental Organisations and other relevant
authorities.
An investigation/assessment of environmental baseline conditions including: Land and soil;
Air quality and noise environment;
Surface water;
Underground water and quality;
Occupational health and safety;
Public health and safety;
Traffic, road safety and public access;
Local Ecosystem, vegetation and habitat; Land use/ Aesthetics;
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Employment and multiplier effects
Other environmental concerns addressed by the proposed project include;
To identify major activities of the project that shall interact with the environment, also
called environmental aspects.
To comply with the Zambian legal requirements.
To provide a platform to the local people and other Interested and Affected Parties (IAPs)
to suggest how best the mine should operate and how they shall benefit.
To highlight key environmental management costs expected throughout the project life
cycle.
1.3
OBJECTIVES
1.3.1 The Project
The main objectives of the proposed project are;
Develop a project into a major open pit tin mining
Mining Tin Ore for commercial use
Running and operating a profitable Tin mine
Creating wealth for both the shareholders and workers
Improving the welfare of the local people
Providing jobs to the local people living in the vicinity of the proposed project site
Enhancing social and security services through corporate social responsibilities
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1.3.2 The EIA
The objective of the EIA is to provide relevant details of the Project, the potential impacts and
proposed management measures to minimise and control any potential adverse impacts. The
information provided in the EIA should enable the environmental acceptability of the project to
be assessed. The specific aims of this EIA are:
To identify and evaluate the environmental impacts that will be caused by the
construction and operation, and may be caused by the continued operation, of the
mine.
To identify and describe procedures and activities that will mitigate adverse
impacts and enhance any beneficial effects.
To make recommendations on how mitigation measures should be incorporated
into the operation and decommissioning stages of the project as appropriate.
To produce an environmental management plan that summarises the impacts and
mitigation measures in a formalised way, and designates responsibility for each of
them. This will help ensure that items identified in the EIA are taken forward and
incorporated into the operation and decommissioning stages as appropriate. It will
also incorporate recommendations for on-going monitoring.
Providing necessary information to the local people, Mines Safety Department
(MSD), Zambia Environmental Management Agency (ZEMA) and Kalomo
Municipal Council for decision making.
1.4
THE COMPANY/CONTACT DETAILS
Rosinvest Zambia Limited is a Private Joint Venture Company between Daled Mining Limited
and Vidayu Holdings Corporation Zambia Limited. It was registered by the Republic
Government of Zambia as a Private Limited Company on the 26th day of February, 2014 with
the Company Registration No. 120174. The company has two company shareholders Daled
Mining Limited with 50% of shares and Vidayu Holdings Corporation Limited with 50%.
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ROSINVEST -EIS
DEVELOPER’S CONTACT DETAILS:
ROSINVEST ZAMBIA LIMITED,
PLOT 66B CENTRAL STREET,
JESMONDINE,
LUSAKA, ZAMBIA.
CELL: 0977 808008
EMAIL: info@rosinvest.co.zm
Table 1:
Particulars of Shareholders
Names
Address
No. of
Shares%
Shares
Daled Zambia Limited
Box 320112 Woodlands Lusaka,
2,500
50%
2,500
50%
5,000
100%
Zambia.
Vidayu Holdings Corporation (Z) P.Bag E 017, Cross Roads, Lusaka,
Limited
Zambia
Total
Table 2:
Details of Directors
Names
Address
Description
Mr. Rustem Nuriev
6786, Chiwalamabwe, Rd, Olympia
Director
Mr. Eldar Nuriev
6786, Chiwalamabwe, Rd, Olympia
Director
Mr. Yury Zhukov
Central Street 66, Jesmondine
Director
Mr. Edward Simukonda
5176, Chishango Road, Villa Elizabeth
Director
Mr. David Bowa
5176, Chishango Road, Villa Elizabeth
Director
Mr. Ali Ismail
5176, Chishango Road, Villa Elizabeth
Director
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1.5
ROSINVEST -EIS
TRACK RECORD/PREVIOUS EXPERIENCE OF THE PROJECT
DEVELOPER
Rosinvest Zambia Limited was incorporated into the Zambian Laws on 26th day of February,
2014 as a Private Joint Venture between Daled Mining Limited and Vidayu Holdings
Corporation Zambia Limited. Apart from mining the shareholders of the company are involved
in other business ventures such as Industry, Agriculture, Construction and Transport.
At a higher level, the Director of Mine for Daled Mining Limited (one of the directors for
Rosinvest) has experience in mining industry. He has worked as an Inspector of Mines. His
duties involved inspecting underground and surface working environment; enforce the provision
of mining; dumps, explosives and environmental regulations. Inquiries into fatal accident, give
evidence at inquests hear cases related to contravention of mining and explosives regulation and
take appropriate action. Investigate dangerous or defective practices, instructs more management
to discuss problems pertaining to matters of safety and health, participates in mine rescue
meeting and evaluates mine rescue exercises.
1.6
COMMENCEMENT OF THE PROJECT
The project will commence upon the approval of the project by the Zambia Environmental
Management Agency (ZEMA) and other Government Institution e.g. Ministry of Mines.
1.7
THE EIA STUDY
The Project falls under the Environmental Management Act (EMA) No.12 of 2011 of the
Environmental Impact Assessment (EIA) Regulations and it is therefore a requirement that an
Environmental Impact Assessment (EIA) study is carried out for the project. The Environmental
Impact Statement (EIS) presents the findings of the study to identify both positive and negative
impacts together with recommendations to mitigate potential negative impacts and to enhance
benefits.
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1.8
ROSINVEST -EIS
SCOPE OF THE EIA STUDY
The EIA study has been carried out following the guidelines and requirements of the Zambia
Environmental Management Agency (ZEMA) and the project Terms of References. The final
document of the EIA study comprises an Environmental Impact Statement (EIS) and an
Environmental Management and Monitoring Plan (EMMP).
Geographically the study is limited chiefly to the mining area Chirobi Village of Mapatizya
Constituency Kalomo District and neighbouring areas such as Choma District and Southern
province at large although effects on issues such as traffic, sources of raw materials and socioeconomic effects may have implications further afield.
From the outset it should be mentioned that one of the major environmental concerns that has
been addressed by the study, and as expressed by neighbouring residents to the project, is the
issue of Noise and Air Pollutions.
Other important environmental issues that have been addressed by the study include:
Water pollution control: management of sewage, solid waste and other waste products as
well as the storage and handling of petroleum products especially during mining
construction and operation.
Public health issues including waste management, HIV/AIDS and vector control
Road access and traffic.
Land use, aesthetics and urban development.
Socio-economic issues including employment and multiplier effects.
The Environmental Management and Monitoring Plan (EMMP) outlines duties and
responsibilities of the developer, Company and other relevant parties to serve as a management
tool in the successful implementation of recommended mitigation measures and subsequent
monitoring thereof during all project phases.
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1.9
ROSINVEST -EIS
METHODOLOGY
The study consisted of three main phases as follows:
Phase 1:
Preliminary actions and scoping exercise
Phase 2:
Baseline studies and data collection
Phase 3
Impact Assessment (of Bio-physical and Social-economic environment during
Construction and operational phases) and recommendations.
Formal review of the EIS document by ZEMA (including public review) follows as the final
main stage in the EIA process.
1.9.1
PHASE 1: PRELIMINARY ACTIONS AND SCOPING
Information regarding the proposed project was reviewed and a pilot survey was conducted of
the study area in order for the study team to obtain an initial appraisal of the environmental
issues involved. Various alternatives for development of the project were discussed with the
developer. The legal and institutional framework applicable to the project was also reviewed at
this stage. From this the team made a preliminary identification of all environmental impacts that
could potentially arise as a result of implementation of the project.
A scoping process was then conducted to determine potentially significant issues that would
form the basis of the EIA study to be included in the Terms of References (TORs), and to
exclude issues unlikely to be of any significance. In order to ensure that public views were taken
into account in the preparation of the TORs, a public consultation (scoping) meeting was held at
in Chirobi Village which was attended by relevant Government agencies, local authorities, and
local residents as well as other interested and affected parties.
The agenda of this meeting included a presentation of the proposed project by Rosinvest Zambia
Limited and project professional team with questions and answers followed by an outline by the
Consultant of anticipated impacts and proposed mitigation measures with an open floor
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discussion. A full attendance list and minutes of the meeting are included in the in the Terms of
References.
TERMS OF REFERENCE
The Terms of Reference were drawn up from discussions within the EIA study team taking into
consideration the issues contained in the Third Schedule of the EIA guidelines and results of the
public consultations. The scope of the study as described by the Terms of Reference is
summarized in Section 1.8 and a copy of the full Terms of Reference will be attached as
annexure 3.
1.9.2
PHASE 2: BASELINE STUDY AND DATA COLLECTION
The baseline study included the following tasks:
A desk study was undertaken wherein the Consultant concentrated on available data,
documents and literature with information relevant to the study. References will be
incorporated in the final document.
Several field trips / surveys were conducted by the study team at the mine and
surroundings to gather information on the existing environment including topography,
geology and soils, fauna and flora, population and settlement, economic activities and
existing physical infrastructure relevant to the environmental study.
Continued consultation was undertaken as necessary with government agencies, other
stakeholders and members of the community to collect data and identify qualitative issues
associated with the proposed project.
From the above a baseline description of the bio-physical and socio-economic setting of the
study area was formed.
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1.9.3
ROSINVEST -EIS
PHASE 3: IMPACT ASSESSMENT AND RECOMMENDATION
An assessment of potential positive and negative impacts resulting from implementation of the
proposed project was undertaken taking into consideration the technical description of the
proposed project and baseline information of the existing environment. Assessment was
undertaken through discussions within the study team and based on a combination of objective
and subjective experience and professional judgment. Further consultations with relevant
agencies / bodies / experts were undertaken as found necessary to assist in this process.
Potential impacts, both positive and negative, were identified and their significance assessed with
the help of the following criteria (as applicable):
Likelihood of impact occurring
(L)
Magnitude / intensity
(M)
Extent (spatial area to be affected)
(E)
Duration
(D)
Frequency
(F)
From this, mitigation measures could be identified and recommended to be incorporated into the
design, implementation and operation of the project so as to minimise, compensate for, or avoid
the occurrence of potential negative impacts or to enhance positive effects. This includes advice
on management clauses to be included in the contractual scope of works.
Mitigation measures and recommendations as well as parameters to be monitored, timing and
responsibilities, are outlined in the EMMP that constituted the final stage of document
preparation.
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2.0
ROSINVEST -EIS
LEGAL AND POLICY FRAMEWORK
This section describes social and environmental laws and institutions that shall be significant to
the Rosinvest Zambia Limited Tin project. This section shall also form the basis for development
of the environmental and social management legal register for the mine. The section briefly
describes the applicable law and explains the relationship to the project.
2.1
BRIEF HISTORICAL BACKGROUND OF THE LEGAL AND
POLICY FRAMEWORK IN ZAMBIA
Due to the requirement for development which meets the needs of today‟s generations without
compromising the needs of future generations, the Government of the Republic of Zambia
(GRZ) adopted the National Conservation Strategy (NCS) in 1985. This was upgraded to the
National Environmental Action Plan (NEAP) in 1992 with the same aim of fostering sustainable
development. The NCS and NEAP are the foundation pillars of environmental laws in Zambia.
The NCS facilitated development of the Environmental Protection and Pollution Control Act
(EPPCA) in 1990 which led to formulation of the Environmental Council of Zambia (ECZ) in
1992. The EPPCA was repealed in 2011 into the Environmental Management Act No. 12 of
2011, which is the current supreme environmental management law. Consequently, ECZ was
changed to Zambia Environmental Management Agency (ZEMA) following repeal of the
EPPCA.
Likewise, the supreme environmental regulatory institution in Zambia is ZEMA, previously
called ECZ. This institution has the legal mandate to enforce provisions of the Environmental
Management Act with its subsidiary regulations. Further to this, the institution has the mandate
to create environmental management awareness and play an advisory function to both the private
and public sectors.
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2.2
ROSINVEST -EIS
THE ENVIRONMENTAL MANAGEMENT ACT NO. 12 of 2011
As highlighted above, this Act was immediately preceded by the Environmental Protection and
Pollution Control Act No. 12 of 1990. Provisions of the Environmental Management Act require
that all new projects begin with an Environmental Impact Assessment (EIA) and after project
implementation; follow-up activities such as licensing, auditing and compliance inspections are
done. These follow-up activities are conducted in accordance with provisions of applicable
Regulations. The Environmental Management Act also provides regulatory instruments for
activities such as, but not limited to waste management, water pollution, air pollution, chemicals
management and hazardous waste management.
Relevance to the Project: - All developments, whether small scale mining or large scale mining
have positive and negative environmental impacts. It is important to identify these impacts in
order to know management measures for mitigating negative impacts and promoting positive
impacts. The Environmental Management Act provides the general guiding principles for
environmental protection and pollution control. It is the umbrella regulatory tool for
environmental management issues in Zambia and all development activities with environmental
aspects have to comply with provisions therein hence the relevance.
Applicable Regulations under the Environmental Management Act No. 12 of 2011 are described
below.
2.2.1 Air Pollution Control (Licensing and Emissions Standards) Regulations of 112 of
2013 Part 2 (SI No. 3).
These Regulations provide air quality standards and guidelines for mitigating air pollutants. The
regulations gave both point source standards and non-point source standards.
Relevance to the Project: - Aspects that shall contribute to air pollution shall mainly be in form
of dust generation from the pit, from overburden dump and from access roads. Earth moving
machines shall also contribute to air pollution from exhaust fumes although regulations are not
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yet developed for mobile emission sources. The project activities described herein will not have
significant point source emissions but ambient air shall have to be monitored especially dust
particulates hence the relationship to the project.
2.2.2
Water Pollution Control (Effluent and Waste Water) Regulations, 112 of 2013
Part 2 (SI No. 3).
These Regulations provides for control of water pollution by providing effluent discharge
standards. Ground water standards are basically established after collecting a set of monitoring
results as baseline and this is specific to the area under consideration. The Regulations also
provide requirements for licensing all effluent discharge points.
Relevance to the Project: - Storm water shall be generated and other effluents in form of
overflow from settling ponds, sewage and from washing of machinery shall be generated. The
effluent from project activities shall not be discharged without obtaining applicable licenses
which are issued with conditions. Therefore, these Regulations are relevant to project.
2.2.3
Waste Management (Licensing of Transporters of Waste and Waste Disposal
Sites) Regulations, 112 of 2013 Part 3 (SI No. 10).
Under these Regulations, activities relating to waste management such as waste generation,
collection, storage and disposal are regulated. The Regulations are only applicable to nonhazardous waste.
Relevance to the Project: - Environmental aspects associated with waste generation are
provision of food to employees, housekeeping activities and removal of overburden material
from the open pit. To manage these wastes accordingly, adherence to the Waste Management
Regulations is relevant hence the relationship to the project.
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2.2.4
ROSINVEST -EIS
Hazardous Waste Management Regulations, 112 of 2013 Part 4 (SI No. 18).
These Regulations do not cover non-hazardous waste. The Regulations control and monitor the
generation, storage, transportation, pretreatment, treatment disposal, export, import, transit, trade
in and Trans boundary movement of hazardous of all waste.
Relevance to the Project: - Rosinvest will hire a generator, light vehicles and earth moving
machines from the local suppliers which will be operating on the site. These machines require
frequent servicing and this leads to generation of hazardous waste. Further to this, used
fluorescent tubes will be generated. All these wastes have to be managed in a manner that would
not cause harm to human health and the environment hence the relevance to the project.
2.2.5
Pesticides and Toxic Substances Regulations, 112 of 2013 Part 5 (SI No. 31)
This provide for ZEMA to regulate the use and importation, exportation and manufacturing of
pesticides and chemicals in the country.
Relevance to the Project: -The proposed project will comply with these regulations.
Appropriate permits will be sought from ZEMA prior to implementation of the proposed project.
In addition, the storage areas will be bundled and upraised to contain any spillage and washing
from the toxic substances emanating from the proposed facilities. An impervious lining will be
laid on the floor to contain leaks. Further, a leak detection system will be put in place.
2.2.6
Noise Pollution
Noise will be generated by the moving vehicles and Mining equipment during operation.
However the noise will be localized by properly servicing vehicles and that the silencers are in
good condition. Any operations, which result in undue noise disturbance, will be restricted.
Signage will be put up to remind workers not to make noise during operation stages whilst on
site
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2.3
ROSINVEST -EIS
THE MINES AND MINERALS DEVELOPMENT ACT NO. 7 of 2008
Besides the Environmental Management Act No. 12 of 2011, environmental issues associated
with mining activities in Zambia are also regulated by the Mines and Minerals Development Act
(MMDA) No. 7 of 2008. The enforcing institution of the MMDA is the Mines Safety
Department (MSD). Provisions of this Act entails that for all mining related projects, the
Factories Act CAP 441, which provides a framework for developing and enforcing regulations to
ensure the safety, health and welfare of persons employed in factories does not apply to the
mining industry. This is to avoid duplicity in law since most of the provisions are already
covered by the MMDA.
Requirements of the MMDA include conducting scheduled inspections, audits, appointment of
competent persons to oversee mining related activities and submission of periodic statutory
returns to MSD.
Relevance to the Project: - The Act provides key safety requirements in the mining industry,
environmental management requirements as well as mine development and mineral processing
requirements. The project under consideration is a typical open pit mining project with
associated support facilities hence provisions of this Act are applicable.
Subsidiary Regulations under the MMDA, which are relevant to Rosinvest Zambia Limited, are
described below:
2.3.1
The Mines and Minerals (Environmental) Regulations of 1997 (SI No 29):-
These Regulations provide a framework for conducting and reviewing EIA reports for all mining
related projects. Further to this, it provides follow-up activities such as auditing and compliance
inspections. The Regulations stipulates specific issues that must be covered in an EIA report for
a mining project and how such issues must be presented. The review and decision making
process is also outlined in these Regulations. The final decision making for new projects is
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legally done under the auspices of ZEMA but MSD plays a key function and ZEMA may
actually reject a project based on comments from MSD.
Relevance to the Project: - This report shall be submitted to MSD through ZEMA and it shall
be reviewed by MSD in accordance with provisions of the Mines and Minerals (Environmental)
Regulations. MSD will also have a duty to conduct inspections in accordance with their legal
mandate. Compliance with these Regulations is therefore very important hence the relevance.
2.3.2
Mines and Minerals Environmental Protection Fund (EPF) Regulations (SI No.
102 of 1998)
These Regulations provides the mechanism for setting up and operating the EPF as an
environmental protection security fund. The fund is managed under the auspices of the Ministry
of Mines and Minerals Development (MMMD) as a security fund for post-mining environmental
liabilities. The Regulations provide for periodic audits to be conducted and includes an
assessment of environmental management costs. Depending on the quality of environmental
management, specifically progressive rehabilitation activities in place, a percentage of the
security fund required to be contributed is proposed and once approved, the mining company in
question pays the stipulated contribution annually.
Relevance to the Project: - It is a legal requirement that all mines contribute to the EPF as a
security fund. The Regulations also demand for periodic audits by mining firms in accordance
with the EPF information requirements. Rosinvest Zambia limited, being a mining project is
fully subjected to these provisions and shall have to continue complying with these Regulations
hence the relevance.
2.3.4 The Explosives Act No. 10 of 1974
The Act defines explosives and the raw material used for manufacturing of explosives. It further
provides guidelines for manufacturing, storage, transportation, distribution and use of all
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explosives and related products/accessories in Zambia. Safety issues are the most outstanding in
this Act.
Relevance to the Project: - The mining methods adopted require procurement, transportation,
storage and use of explosives. This will be done under care and maintenance and it shall continue
in accordance with provisions of this Explosives Act and the regulatory institution (MSD) is will
be fully notified.
2.4
THE OCCUPATIONAL HEALTH AND SAFETY ACT NO. 36 OF 2010
Unlike the Factories Act which does not cover the mining industry, the Occupational Health and
Safety Act cover all types of industries in Zambia. It provides general guiding principles for
occupational Health and Safety. For Example, Section 11 of the Act requires that all employers
establish Health and Safety committees.
Relevance to the Project: - Provisions in this Act are more inclusive than the Mining
Regulations and it is a legal requirement for all industries to comply with these provisions hence
the relevance to Rosinvest Zambia Limited.
2.5
THE PNEUMOCONIOSIS ACT NO. 13 OF 1994
The Pneumoconiosis Act provides the Health and Safety regulatory requirements for mining and
related activities carried out in restricted spaces where silica mineral fractions below 5 microns
are likely to be encountered in ambient air. Under this Act, all workers in the mining industry,
especially those that might be exposed to silica must undergo silicosis medical check-ups
annually.
Relevance to the Project: - Workers shall be exposed to silica especially at the pit and the
Overburden Dump. Dust can also be a potential source of silica. Therefore, all workers shall be
subjected annually to silicosis test in accordance with provisions of this Act. Therefore, the
Pneumoconiosis Act is relevant to the operations at mine.
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2.6
ROSINVEST -EIS
THE NATIONAL HERITAGE CONSERVATION COMMISSION ACT
The National Heritage Conservation Commission Act CAP 173 of 1989 stipulates preservation
and protection of ancient cultural and natural heritage resources and objects of aesthetic,
historical and archeological value. In this Act, “Ancient Heritage is defined as being among other
things, any structure, settlement previously inhabited, land mark, burial place or any other item
designated by the commission which is known or believed to have been erected, constructed or
used before 1st January 1924. The Act also provides for the formation of the National Heritage
and Conservation Commission which is the responsible institution.
Relevance to the Project: - In order to protect national heritage resources in the project area, it
is important to conduct any activity in accordance with provisions of the National Heritage
Conservation Commission Act. The project is located in the area gazetted for and all activities
are regulated. However, any resource of national heritage importance has to be protected hence
the relevance.
2.7
THE ROAD TRAFFIC ACT
The Road Traffic Act No. 11 of 2002 was enacted to cover issues of road safety in Zambia. The
Act provides for establishment of the Road Transport and Safety Agency (RTSA) and defines
functions of RATSA. It also provides for a system of road safety and traffic management.
Relevance to the Project: - Access to the site is through feeder roads that are used by other road
users. There are also settlements along these feeder roads, which is common for all rural roads in
Zambia. It is therefore necessary to adhere to road traffic requirements in order to safeguard the
health and safety of other road users.
2.8
THE FOREST ACT CAP199 OF 1973
The Act provides for establishment, gazetting and de-gazetting of forests. It also provides for
monitoring, forest inventories, management and regulation of forest areas and forest products,
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nationwide, and particularly in National and Local Forests. The Act is enforced by the Forest
Department Specific to the general protection of forest resources, the Act provides for protection
of Six (6) tree species in Zambia whether in a protected area or outside. These tree species are:
Afzelia quanzensis (Pod Mahogany)
Baikiaea plurijuga (Teak)
Entandrophragma caudatum (Mountain Mahogany)
saligna (Beech wood)
Khaya nyasica (Red Mahogany)
Pterocarpus angolensis (African Teak)
Relevance to the Project: - The site is surrounded by an intact forest, apart from the already
cleared potion for mining. It is necessary to protect the area surrounding the site especially
within the mining license area. In addition, adherence to provisions of the Forest Act is relevant
to protection of the species listed above and any other forest resources around the project area.
2.9
THE ZAMBIA WILDLIFE ACT, NO. 12 OF 1998
The Zambia Wildlife Act No. 12 of 1998 provides for establishment of the Zambia Wildlife
Authority (ZAWA) and provides for the sustainable management of wildlife resources in
Zambia. The Act also provides for regulation of all wildlife activities such as hunting, poaching
and keeping of wild animals. The local management of wildlife resources and habitats is partly
delegated to Community Resource Boards (CRBs) in designated Game Management Areas
(GMAs). The CRBs in turn are given commission for the income generated from GMAs and this
technique has so far proved to be a success.
Relevance to the Project: - The existing ecosystem within the project area has potential for
existence of wild animals although most of the big animals have migrated from the area. In order
to protect wild life resources, it is important for Rosinvest to comply with provisions of the
Zambia Wildlife Act hence the relevance to the project.
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2.10
ROSINVEST -EIS
THE FISHERIES ACT OF 1974
The Act regulates all fishing activities in Zambia undertaken in any kind of aquatic ecosystem.
This includes lakes, rivers and streams. It also regulates activities that may interfere with
fisheries such as discharge of pollutants into aquatic ecosystems. The implementing institution
for this Act is the Ministry of Fisheries and Livestock.
Relevance to the Project: - The nearest stream to the project site in Siankopo area is in the east
side of the license area which drains into the Tabana River about 500 m in north east of the site.
Another stream in the Siankopo area about 3km from the site in south east is Singewso River.
Baseline assessments revealed that the stream does not have fish stocks of significance.
However, it is necessary to understand provisions of the Fisheries Act to avoid legal noncompliances especially that there are water bodies near and around the project area.
2.11
THE PETROLEUM ACT CAP 439 AND THE ENERGY REGULATION ACT
CAP 436
The Petroleum Act provides for control of conveyance and storage of petroleum products such as
diesel and petrol. The Act further provides for control measures regarding production,
transportation, handling, distribution, re-sale and use of energy in Zambia.
The Energy Regulation Act of 1995 makes provision with respect to the production and
distribution of energy in Zambia and establishment of the Energy Regulation Board (ERB) for
purposes of control and licensing of energy undertakings. In accordance with this Act, ERB
shall, in conjunction with other Government agencies, formulate measures to minimize the
environmental impacts of transportation, storage and use of fuels and enforce such measures by
attachment of appropriate conditions to licenses held by such undertakings.
Relevance to the Project: - Mining machines and the generator shall require fuel in large
quantities. This fuel shall be obtained from various fuel suppliers. Even if an above ground fuel
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ROSINVEST -EIS
storage facility shall be constructed, transportation and refueling has to comply with provisions
of the Energy Regulation Act hence the relationship.
2.12
TOWN AND COUNTRY PLANNING ACT CAP 475 OF 1962
The Town and Country Planning Act came into force in 1962. It provides for the establishment
of planning authorities (Councils) and the preparation, approval and revocation of development
plans. It further provides for the control of development in a district and the subdivision of land.
The zoning and rezoning of areas must comply with the provisions of this Act. Environmental
Impact Statement for Rosinvest is in Kalomo District Southern Province of Zambia.
Relevance to the Project: - Rosinvest Zambia Limited falls within the jurisdiction of Kalomo
District Council and all planning and land use development activities are regulated by this
Council. The Council is constantly engaged in development activities and Rosinvest shall
continue with this relationship as a way of ensuring that activities are compliant with the Act.
2.13
THE LOCAL GOVERNMENT ACT OF 1991
The Local Government Act CAP 474 of 1991 provides for a system of local government
administration in Zambia at city, municipality and district Council levels. Each local governance
level has delegated statutory functions with respect to development planning. The Act also
allows Councils to implement environmental protection and natural resources management
functions which include prevention of pollution of water supplies and has some control in
undertaking of mining operations.
Relevance to the Project: - As already stated the project is located in Kalomo District which is
the implementing institution of the Act. In accordance with this Act, all construction engineering
drawings and site plans must be approved by the Local Authority before construction.
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2.14
ROSINVEST -EIS
PUBLIC HEALTH ACT CAP 295 OF 1978
This Act provides for prevention and suppression of public health hazards. It regulates all
matters and activities that are connected to outbreak of diseases. Local Authorities, in this case
Kalomo District Council is the custodian of the Public Health Act. Provisions of the Act are
implemented by Councils through licensing and inspections.
Relevance to the Project: -Wherever human activities take place, issues of public health are
critical. Environmental aspects of the project that shall require adherence to the Act include
provision of waste management facilities, sanitation facilities, food, shelter, pest control services,
drinking water storage and food storage facilities. To ensure that issues of public health are
understood, implemented and sustained, the Public Health Act is relevant to the proposed
project.
2.15 LANDS ACT CAP 29 OF 1995
The Lands Act controls all matters pertaining to the management/use of land and land tenure
systems. The process of acquiring the mining license exhausts part of the applicable land
acquisition laws.
Relevance to the Project: -The project is being implemented on land that falls with Chiefdom
Simwata Chela within Kalomo District. For land acquisition and surface rights, provisions of the
Lands Act do hereby apply hence the relevance.
2.16
EMPLOYMENT ACT CAP 268
This Act provides conditions under which employees should work in Zambia. The Act covers
both temporary and permanent employees. Generally, this Act talks about employee protection
and social security requirements. Major provisions include:
Minimum contractual age;
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Establishment of employment contracts;
Settlement of disputes arising from such contracts of employment;
The appointment of Labor Officers and other staff for the administration of the Act; and
Certain conditions of employment such as ordinary leave, sick leave, maternity,
redundancy and welfare of employees.
Relevance to the Project: - One of the significant positive impacts of the project is creation of
job opportunities to the local people. Whenever labor issues are involved, provisions of the
Employment Act are critical hence the relevance of the Act to the project.
2.17
THE WATER SUPPLY AND SANITATION ACT NO. 28 OF 1997
The Water Supply and Sanitation Act provides the regulations and standards applied in the
provision of public water and sanitation services. It also provides for permitting of water supply
and sanitation service provision.
Relevance to the Project: - Domestic water will be provided to workers at the project site and
this water will meet the minimum quality standards. This report therefore acknowledges this fact
for compliance hence the relevance to the project.
2.18
THE WATER ACT, CAP 312 OF 1948
The Water Act provides the control process for the abstraction of water from surface sources.
The Act is currently being revised as an Integrated Water Resources Management Act that will
widen its influence to include groundwater. The Act further provides for the right to access
public water and restricts public access prohibiting activities around public water sources such as
rivers.
Relevance to the Project: - Water abstraction activities require permits from the Water Board
through provisions of the Water Act. Currently, no permits are obtained and through
implementation of this report, all applicable water abstraction and use permits shall be obtained.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
2.19
ROSINVEST -EIS
MINIMUM WAGES AND CONDITIONS OF EMPLOYMENT ACT (CAP 276)
This Act stipulates the minimum conditions of service for permanent as well as casual workers.
It further provides the minimum monthly wages for different categories of workers and defines
workers who are exempted from the wage categories.
Relevance to the Project: - When jobs are provided, labor related issues should also be
followed to strike a balance between employees and the employer. The Act actually protects both
parties and its provisions are very much applicable to the project.
2.20
WORKERS COMPENSATION ACT No. 10 OF 1999
This is a social security Act which has provisions for employee compensation in case of injury or
death of an employee whilst at work. It is a requirement under this Act that all employers register
their employees with the Workers Compensation Fund and make periodic subscriptions for
compensation of their employees.
Relevance to the Project: -The mining industry is not exempted from provisions of this Act.
Considering the fact that job opportunities will be provided by Rosinvest Zambia limited, a
detailed understanding and adherence with requirements of the Workers Compensation Act.
2.21
INTERNATIONAL CONVENTIONS AND PROTOCOLS
Among the most relevant environmental conventions are; Convention dealing with the Protection
of the World Cultural and Heritage (1972) and ratified by Zambia in 1982, Statutes of the
International Union for the Conservation of Nature and Natural Resources (IUCN). Others
include Convention on Biological Diversity (1992) ratified in 1993 and the RAMSAR
Convention. Below are some of the applicable international conventions;
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
2.21.1
ROSINVEST -EIS
Convention on Biological Diversity (CBD)
The major aim of the CBD is to effect international cooperation in the conservation of biological
diversity and to promote sustainable use of natural resources worldwide. It also aims at bringing
about sharing of the benefits arising from utilization of natural resources. A number of plans in
this convention fall under the Departments of Agriculture, Forestry, Fisheries and ZAWA.
Relevance to the Project: - All wildlife conservation activities in this report are aimed at
implementing best practices for environmental management. Therefore, adhering to local laws
and complying with the CBD provisions is relevant. For this, provisions of the CBD are relevant
to the project.
2.21.2
Ramser Convention
The general objective of the Ramser Convention is to curtail the loss of wetlands and to promote
wise use of all wetlands. The convention addresses one of the most important issues in Southern
Africa, namely the conservation of water supplies and use of the natural and the human
environments in responsible manner for intergenerational benefit.
Relevance to the Project: - Wetlands provide a wide range of resources and services ranging
from pollution control as a service and water provision as a product. The nearest wetland to the
Mine is Lake Kariba. It is therefore imperative to protect these water resources as a conservation
measure and a way of complying with the above cited Convention hence the relevance to the
project.
2.21.3
Convention on International Trade in Endangered Species of Wild Fauna and
Flora (CITES)
The objective of this agreement is to ensure that international trade of wild flora and fauna does
not endanger their existence. The convention is customized through the Zambia Wild Life Act
No. 12 of 1998 and the implementing body is Zambia Wildlife Authority.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Relevance to the Project: - The project area has potential for existence of wildlife and if
protection measures are not strictly enforced, there is likelihood that employees may start
exploiting these resources. Therefore, provisions of this Convention together with the
customizing regulations are critical to the project.
2.21.4
The United Nations Framework Convention on Climate Change (UNFCCC)
It was signed by Zambia in 1992. The main objective is to achieve stabilization of greenhouse
gas concentrations in the atmosphere. Zambia recognizes that the largest source of one of the
main greenhouse gases, carbon dioxide, is from burning wood fuel and the use of coal and oil.
Relevance to the Project: - Just like the Kyoto Protocol, reduction of greenhouse gases is key to
this Convention. Use of petroleum products such as fuel is one of the ways in which carbon
emissions are encountered and there is need to consider these issues during project planning.
This explains the relevance and relationship to the project.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
3.0
BASALINE DESCRIPTION OF THE ENVIRONMENT
3.1
BIO-PHYSICAL ENVIRONMENT AND GEO-ENVIRO
3.1.1
ROSINVEST -EIS
DESCRIPTION AND LOCATION OF THE SITE.
The project site is located in Chiefdom Simwata Chela of Chirobi village, Mapatizya
Constituency of Kalomo District on a Large Mining License No. 16395 – HQ – LGL. The site is
accessed through Mapatizya Gravel Road about 165Km from Mapatizya Junction off Great
North Road (Livingstone Road T2) and is approximately about 40km2.
Fig 3:
Location Map
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Fig 4: Coordinates of the Mine
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ROSINVEST -EIS
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
3.1.2
ROSINVEST -EIS
ECOLOGY
The ecological environment in the project area comprises of (i) terrestrial habitat of primary,
secondary forest, river-line vegetation, (ii) the aquatic habitat of local seasonal streams of which
the main rivers Lake Kariba. It is from this environment where a number of species (flora and
fauna) may be found.
3.1.3
CLIMATE
Chirobi village experiences a modified type of equatorial climate, the mean monthly rainfall
ranges within 0m in the dry summer months to 380mm in the winter part of the year, while the
mean annual rainfall is within 800mm to 1000mm. The mean monthly maximum temperature
ranges within 22°C to 34°C while the mean monthly minimum temperature is in the range of 6°C
to 14°C.
Wind direction in Chirobi is generally from the North West to the south east with occasional
changes in the wet part of the year. Wind speed average 30m/sec in the summer months to
22m/sec in the winter.
The mean monthly evaporation averages around 170mm. Kalomo District has experienced
incidences of extreme weather conditions such as the 1996-1997 drought that affected most parts
of the country causing a number of streams to dry up. The streams are gradually recovering from
the drought in the past two rainy seasons in which the country has received adequate rainfall.
3.1.4
HYDROLOGY
Chilobe stream crosses the edge of the site in the eastern direction while Chana stream is about
4km south of the site as shown in figure 6 and the attached annexure 7. This pattern of the two
streams in the area assumes adequate opportunity for infiltration and downward percolation in
the upland soils, allowing only minor runoff. However, during the study, it was noted that within
the area there were some pockets that had unsteady flow systems (Dambos and depressions),
44
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
where hydraulic gradients and moisture contents were varying with time. This kind of scenario
was noted on the land set imagery. Upon triangulation it was noticed that the variation was
associated with soil differences and this usually resulted in variation of vegetation types. It was
also observed that in the Dambos and depressions, vegetation and/or tree cover was not dense;
this could be due to poor drainage -where trees are not able to cope with water logged conditions.
3.1.4.1
SURFACE WATER FEATURES
The area is rapidly draining and has a number of perennial streams serving it. The nearest
streams to the mining license area include Chilobe stream which partially passes the license area
and Chana stream which passes about 4km south of the site. Figure 6 below shows the nearest
streams to the license area.
Fig 5: Nearest Streams to the License Area
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
Not much significant work has been done so far, to ascertain the depth, presence and quality of
ground water but the area holds promise that the water table is nearly 50-65m below the surface.
Fig 7: Surface Water in Chirobi Area during Rainy Season
3.1.4.2
UNDERGROUND WATER RESOURCES
While rainfall is the primary contributor usually the rainfall provides sufficient recharge facility
for the aquifer although seasonal groundwater level fluctuations occur according to rainfall
received. Levels go down between May and November and rise between December and April
during the rainy season.
The area is well drained with surface water streams which is unsuitable for human consumption.
The ground water table is estimated at around 50-65m below the surface, the quality is expected
to be good and suitable for domestic use.
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3.1.5 GEOLOGY AND GEOMORPHOLOGY
According to general survey map and study by the Geological Survey Department of Zambia
(1992), the regional geological description of the area where the project falls is dominated by a
granitic dome centred to the south of Kalomo town. The rock formation mainly consists of
calcite and dolomitic marbles. Others are a geological formation called pelitic formation, mainly
consisting of biotite schists, phylittes, calcareous and graphite slates. Ground elevations within
the project vary between 520 and 1,000 meters (M) above sea level (AMSL).
The proposed area lies within a basement complex zone mainly underlain by the gneisses and
schists. These rocks are intruded by the quartz-muscovite-feldspar-tourmaline pegmatites and
dolerite dykes. In some places these are cassiterite-bearing while in some they are not. In many
cases these pegmatites form hills for instance at Kapongo Hill. Tin occurs in form of cassiterite
(SnO2) as eluvial and alluvial, predominantly eluvial. In hand specimen it looks massive or as
tetragonal crystal with a sub metallic black colour and is heavy.
The geological survey of the proposed area was conducted and the chemical analysis reveals the
results as shown below:
Table 3
Sample
Id
Chemical analysis results (done by MABVUTO MWALE)
Location
X
coord
Y coord
Element (%)
Mn
Fe
Cu
Zn
Ta
Pb
Zr
Nb
Sn
Co Ti
LE
HM5R/side
479122 8057023 -
-
-
-
0.312 -
-
0.235 21.08
-
-
-
ChiseR/TaHM4
483250 8056833 -
-
-
-
0.105 -
-
0.073 6.607
-
-
-
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HM6V/high
ROSINVEST -EIS
478831 8056750 -
-
-
-
0.892 -
-
0.708 74.580 -
-
-
Dobolobo 483348 8059428 I T1
-
-
-
-
-
-
-
0.1
-
-
-
HM1
482619 8060083 -
-
-
-
-
-
-
-
-
-
-
-
HM3
486161 8055670 -
-
-
-
-
-
-
-
-
-
-
-
Maboono 483284 8060323 pit 3
-
-
-
0.495 -
-
0.359 85.69
-
-
-
S7Dobo2
483430 8059251 -
-
-
-
-
-
0.618 0.001
-
-
-
Grave
483161 8056297 0.33 14.11 -
Maboono 483298 8060178 0.52 3.08
pit 1
0.24 0.04
0.16 0.19 0.79
-
0.03
0.02
0.10 0.10 0.63
1.64
94.44
0.52 83.05
-
-
According to the results obtained from the chemical analyses of the ore (table3), the grades for
tin (Sn), Tantalum (Ta) and Niobium (Nb) range from 0.001%Sn [S7] to 94.44%Sn [Maboono];
from 0.04%Ta [Grave] to 0.892%Ta [HM6] and from 0.02%Nb [Grave] to 0.708%Nb [HM6].
From the results so obtained the average values in the entire study area are:
Ta:
Nb:
Sn:
0.439%
0.378%
35.51%4
Fig 6: Geology of the Area
48
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Figure 7: Map showing the general geological layout of Zambia.
3.1.6 TOPOGRAPHY
Four elevation points recorded with a Global Positioning System (GPS) receiver around the
project area gave an average elevation of 1403 meters above mean sea level. A walk around the
project area for a distance of 1000-1300m indicate water bodies and interviews with the field
guide explained that there were seasonal streams within a radius asked of about 5 km.( See
Topographical Map in Annex 20).
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Figure 8:
3.1.7
ROSINVEST -EIS
Topography at the proposed Site
LANDSCAPE
The landscape is naturally gentle with depressions only where there are water bodies and most
elevations where there are anti-hills. From the field assessment, anthills in the area cover about
10% of land and these are on average about 7 meters high and are covered by a variety of
vegetation species.
Considering the average elevation recorded for the area, it is clear that the mine is on a higher
flat land hence the reasons why there are water bodies nearby.
3.1.8
SOILS
The soil classification conducted by Mount Makulu Agriculture Research Station in 1983 for
Kalomo district indicates the following generic soil types in the catchment area.
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ROSINVEST -EIS
Gleyic Cambrisol: - This soil type mainly occurs in dambo areas. This has a relatively
fertile top soil but it usually gets waterlogged in the rainy season.
Xanthic Ferrasol and Orthic Ferrasol: - These are extremely weathered, deep and well
drained soils. The soil is yellowish in color and the texture is clay.
Ferric Acrisol: - These soils are extremely weathered, well drained and with a fine clay
soil texture.
Constraints for the common soils listed above are shallow rooting depth, nutrient deficiency,
highly leached, low pH and usually have a nutrient imbalance.
The site is characterized by reddish-brown soil varying from sand in the top soil to sandy loam or
clay loam at depth of close to 2m.The area is freely drained. In ridges and hills deep Laterite
stones mantle over weathering grit is evident. The wide valley flows have black to dark brown,
loose schist rocks. Being remote area, soil has predominantly been undisturbed. However, the
specific soil type for the project area is sandy loamy soil.
3.1.9
FLORA
The main vegetation cover is natural vegetative Miombo Woodland. This is the characteristic
vegetation of the Chirobi area. This vegetation type covers some 80% of the country. The term
„Miombo‟ is derived from the plural of „Muombo‟ the Bemba name for Brachystegia longifolia
one of the common dormant species in these woodlands. This plateau Miombo Woodland has an
open and semi evergreen canopy of about 15– 20m.The other species are Chipya and Riparian.
Below is the table of the different species:
Table 4
Species of Area;
Vegetation Type
Common Species
Condition
Miombo woodland –
Brachystegi longifolia, B. boehmii, B. spiciformis, Burkea
Woodland rich in green
Subtype
Africana,
Brachystegia- Burkea
condylocarpon,
woodland
curatellifolia and Pericopsis angolensis
Combretum
molle,
isoberlinia
51
Diplorynchus trees of different sizes
angolensis,
Parinari
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
Miombo woodland –
Anisolphlea
Subtype
spiciformis, Burkea Africana, Parinari curatellifolia, trees of different sizes
Brachystegia -
Phyllocosmus andDiplorynchus condylocarpon
pomifera,
Brachystegia
boehmii,
B. Woodland rich in green
Pteleopsis woodland
Miombo woodland –
Brachystegia spiciformis, Marquesia macroura Uapaca
Woodland rich in green
Subtype Marquesia –
kirkiana, U. bangweolensis
trees of different sizes
parinari woodland
Riparian Forest –
Bridelia micratha, Ficus…,Parinari excels, Uapaca nitida Intact with fires
restricted along the
affecting trees on the
stream
fringes
Chipya woodland
Diplorynchus condylocarpon Julbernadia globiflora,
Intact with little fire
Isoberlinia angolensis, Monotes africanus Pericopsis
effect
angolensis, Phyllocosmos
Figure 9:
Vegetation at the proposed Site
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
3.1.10 FAUNA
The welfare factors which attract wildlife such as water, vegetation cover and sandy areas are
available within the mining area.
Animal life:
There was a variety of wildlife observed ranging from Otolemur crassicaudatus (Bushbaby),
Crocuta (Spotted hyena), Potamochoerus porcus (Bushpig), Cricetomys gambianus (Giant rat),
Paraxerus cepapi (Bush squirrel), Lepus victoriae (Hare), and Sylvicapra grimmia (Common
duiker).
Reptiles
included;
Agama
aculeate
armata,
Hemidactylus
mabouia,
Gerrhosaurus
nigrolineatus, Python sebaenatalensis, Natriciteres olivacea, Psammophis phillipsii and
Philothamnus hopplogaster and Bitis arietans while amphibians included Phrynobatrachus
natalensis and Xenopus laevis pertersii.
Bird life includes:
Globally threatened species in the IBA are:
Lesser Kestrel;
Wattled Crane;
Denham‟s Bustard; and
Black-winged Pranticole.
Species of regional conservation concern are:
Bateleur;
White-Spotted flufftail;
Southern Ground Hornbill;
White-Bellied Bustard;
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
White-bellied Kingfisher;
Brown-eared Woodpecker;
Shrike-Flycatcher;
Margret‟s Batis;
Chestnut Wattle-eye; and
Potted Thrush-Babbler
ROSINVEST -EIS
Other animal species to have once been there are in the table below:
Table 5
Animal Species
Species Local Name
Common Name
Scientific Name
Insefu
Eland
Taurotragus oryx
Inkosa
Hartebeest
Sigmoceros lichtensteinii
Intandala
Kudu
Tragelaphus strepsiceros
Chisuumpa
Leopard
Panthera pardus
Impelembe
Sable antelope
Hippotragus niger
Impelembe
Roan antelope
Hippotragus enquinus
These species are said to be locally extinct. Most common reason for extinction of these animal
species is hunting using, hand-made guns, dug-pits armed with spears and wire snares.
3.2. SOCIO- ECONOMIC AND CULTURAL ENVIRONMENT
3.2.1
DISTRICT BACKGROUND
Kalomo District Council is one of eight Districts of the Southern Province. Other Districts of the
Southern Province are Mazabuka, Monze, Choma, Livingstone, Siavonga, Sinazongwe and
Mulobezi. The district geographical location is 27 10‟ 25 50” Longitudes East and 16 55‟ - 17
30” Latitudes South. The Districts Headquarter is at Kalomo Town 340 Kilometers from Lusaka
city along Lusaka- Livingstone highway. The District is bordered by Choma District to the
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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North, Livingstone District to the South and Mulobezi Districts to the West and to the East is
bordered by Zimbabwe border. It has a about of 20,000 sq kms of which 12000 sq kms of the
area is suitable for cultivation; and 51 sq kms is forest reserve area. Tonga Choma, Kalomo Hill,
Tara and Zimba Hill forest reserve has 15.99 sq kms.
District Council has four (7) divisions namely: Kalomo, Kanchele, Kabanga, Zimba, Siachitema,
Siavwima, Tara and Chikanta. These divisions are then divided into (15) wards, which in turn are
divided into 120 Villages.
3.2.2
GOVERNMENT, ADMINISTRATION AND POPULATION CHARACTERISTICS
Southern Province had a population of 1,606,793 of which 49 percent were males and 51 percent
were females. The population increased from 1,212,124 in 2000.The average annual population
growth rate for the province over the intercensal period 2000-2010 was 2.9 percent. There was a
decline in the growth rate from 2.3 percent in the 1990 -2000 period to 2.9 percent between 2000
and 2010.
The 2010 CSO preliminary statistics indicate that Kalomo District has a total of approximately
254,211people of which 130,886 representing a percentage of 51% are females and 130,886
representing a percentage of 49% males. In the year 2000, the district had a total of 169,503
people as shown in the table below. The 2000-2010 inter-censal average annual population
growth rate stood at 4.1%.
The following table highlights the trend in the population growth rate of Kalomo from the year
2000 to 2010 according the CSO preliminary report of 2010.
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Table 6: Population of Kalomo District (CSO Preliminary Report of 2010)
AVERAGE ANNUAL
DISTRICT
2010 POPULATION
2000 POPULATION
POPULATION GROWTH
RATE, 2000 - 2010
KALOMO
Males
Females
Total
Males
Females
Total
Males
Females
Total
83,175
86,328
169,503
123,325
130,886
254,211
4.0
4.2
4.1
The proposed project area is located in Mapatizya constituency which has a total of 66,725
people 32,186 males, 34,539 females and 13,284 households.
3.2.3
HEALTH/INFRASTRUCTURES
Malaria is the most common sickness in the area followed by diarrhea and respiratory diseases.
Health services are accessed at Kabanga Mission Health Center about 30 km from the mine site.
The Clinic is currently providing almost all the necessary services such as RCHC services level
as farmers sell the crops to customers direct from the farm. Other health center is Simwatachela
Mission Rural Health Center in Kabanga area.
In the Mapatizya area, commercial sex work an outcome of poverty is contributing to a rising
number of HIV/AIDS cases. Migrant traders constitute the main clients for women in this
profession. The RHC has reported + 40 HIV cases and has 10 people under anti. Malaria
accounts for approximately 10 percent of district fatalities and can be attributed to conditions
associated with the low-lying, peri-urban, and unplanned settlements. Generally, malaria,
tuberculosis, HIV/AIDS, malnutrition, and silicosis account for many deaths among the
population.
3.2.4
EDUCATION/INFRASTRUCTURES
The study revealed that the majority in the area have at least stepped into school. Out of these,
said they had attained at least primary school level of education.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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This is closely followed by those who have been to secondary school and attained tertiary
education. A least of those in the area said they have never been to school.
The nearest schools to the area are Misika Basic School and Chalimungela about 10km from the
mining area. Other schools include Chana Community School, Siajina and Kabanga schools.
3.2.5
TRANSPORT, TRADE AND COMMUNICATION
The site is accessed through a gravel road from Mapatizya junction off great north road.
On mine vehicle traffic will be limited and restricted to the developed road network. Two road
ways will be constructed one (1) for public and second (2) for mining equipment.
Footpaths will be kept to a minimum, to prevent the opening up of the mine to too much
uncontrolled activity. This will be done by designating areas that shall be used as foot paths with
specific signs.
Most of the farmers in the proposed project sell their farm produce and buy their daily necessities
at Kabanga market which happens to be the nearest market about 30km from the mine. Others
prefer either Kalomo or Choma.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Figure 10:
ROSINVEST -EIS
Nearest Market (Kabanga Market)
There are no telephone communication lines, though Mobile Cell Networks such as Airtel, MTN
and Zamtel are available.
3.2.6
LAND USE IN THE PROJECT AREA.
The livelihood strategies of the people in project area largely depend on mining, agricultural
fisheries forest products and animal rearing. These activities occupy most of the land use in the
area where Maize is the main crop grown. Other crops grown in medium to small quantities
include groundnuts, beans, sorghum, finger millet, sweet and potatoes. Livestock is a source of
livelihood and it is practiced on a large scale. Animals mostly reared include Cows, Goats, Pigs,
Chickens and Ducks.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Beside Mining, Agriculture, Animal rearing and Fisheries various activities are undertaken such
as handcraft activities, carpentry, wood carving, mat carpet and basket making which are wide
spread and normally are taken as an off farm activities to supplement farm income.
Rosinvest (Z) Limited intends to use the land for Tin Mining and ensure that the demand for Tin
can be met with the favourable economic climate in the country and therefore contribute
significantly to the sustainability of the mining industry with resultant multiplier effects.
3.2.7
LAND OWNERSHIP AND LAND TENURE
The study area falls under Traditional land tenure and it is in Chiefdom Simwata Chela of
Chirobi Village, Mapatizya Constituency of Southern Province of Zambia.
The proposed area is under Traditional Land Tenure. Under this, Chief Simwata Chela through
village headmen provides pieces of land to families and clansmen without title. The Chief and
his/her clansmen communally own land. In a case where conversion of traditional land into lease
is needed, the applicant seeks the consent of the Chief through the Headmen and his subjects
within the area. If the Chief has no objection, Local Authorities process the application and
recommends to the Commissioner of Lands for final approval and offer of the lease.
The mining area under consideration has been gazetted as a Mining Area by the Ministry Mines
and it has been invested in interest of Rosinvest under Large Mining License No. 16395-HQLPL.
3.2.8
WATER AND SANITATION
With regards to sustained access to clean water and sanitation, people in the study area get their
drinking water from hand-dug wells. With the investigation taken in proposed area shows that
the average depth of the hand-dug wells varies as to those in the highland and those in the
lowland. Those on highlands showed an average 8-10m and those on lowlands an average 5-8m.
On the other hand others get their drinking water from the Chilobe and Chana stream. In terms of
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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treatment of drinking water, a few reported that they treated their drinking water with chlorine
while the rest did not.
In terms of sewage management and domestic waste disposal, most use pit latrines and the rest
resort to using the bush. For waste disposal, most respondents stated that they use rubbish pits.
For the proposed project, drinking water and operational use will be obtained from bore holes on
the site. The company envisages sinking 3 bore-holes. Septic tanks shall be constructed for
sewerage disposal and waste bin for domestic waste disposal.
3.2.9
EMPLOYMENT CREATION
The investment would create a number of jobs opportunities in the construction area and more in
the operation phase. About 82 local people are anticipated to be employed for the construction
and operation process for its duration.
The project will employ as follows:
In mining about 60 persons
In concentrator about 12 persons
In smelting about 10 persons
As permanent employment and in temporary bases will be more.
3.2.10 ARCHAEOLOGICAL SITE
The area planned for the project including the access road did not show any unique resource that
could be of historical or archaeological significance. During the field study the access road was
trailed by foot in order to observe any feature of interest in this regard. A transect was also made
across the area and interviews with locals also confirmed that the area has no resources of this
nature.
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3.2.11 SOCIAL-CULTURAL
Rural communities in Zambia are organized on the basis of chiefdoms which are under the
jurisdiction of Chiefs, who have advisors called Indunas. The chiefdoms are divided up in
villages, led by a village headman. Traditionally, the men of the village would gather to discuss
issues of importance until a decision is reached by consensus. In addition, most communities
have a chair lady; an elected female leader who will see to women‟s affairs. Apart from this
person, women are poorly represented in traditional governance and are unlikely to influence or
be informed about decisions made by the village council.
The visited licensed mining area falls within the jurisdiction of traditional authorities. In the case
of Mapatizya, Chief Simwatachela presides over the area. His authority extends to the mining
settlement area and the headman may settle disputes between people in this area when asked to
do so.
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4.0
PROJECT DESCRIPTION
4.1
BACKGROUND, OBJECTIVES AND NATURE OF THE PROJECT
4.1.1
BACKGROUND OVERVIEW
Zambia has a wide range of mineral deposits namely; Copper, Zinc, Manganese, Coal, Amethyst,
Tin, Aquamarine, Silver, Garnet, Tourmaline, Gold etc. The mining industry has been dominated
by Copper and Cobalt. Mines account for 8% employment in the country. Zambia is ranked as
the 5th world‟s largest producer of Cobalt and 12th largest Copper producer. It was also one of
the top producers of Gem-quality Emeralds in 2000. Besides Copper and Cobalt, Zambia
produces Gold, Selenium and Silver as byproducts of Copper Refinery, a variety of industrial
minerals and Coal.
The Tin Belt of the Southern Province of Zambia has a history of small working extending over
Sixty years, with limited production from numerous small eluvia, alluvial and pegmatite deposits,
co-operative tin mining was initiated in 1963, but ceased in 1965 following Rhodesia‟s unilateral
declaration of independence. The Geological Survey Department carried out a study of all known
occurrences in 1967 and 1968 in order to assess the potential of the area as a preliminary to reactivating co-operative mining.
4.1.2
OBJECTIVE OF THE PROJECT
The main objectives of the proposed project are;
Develop a project into a major open pit tin mining
Mining Tin Ore for commercial use
Running and operating a profitable Tin mine
Creating wealth for both the shareholders and workers
Improving the welfare of the local people
Providing jobs to the local people living in the vicinity of the proposed project site
Enhancing social and security services through corporate social responsibilities
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Other Objectives include the following:
To identify major activities of the project that shall interact with the environment, also
called environmental aspects.
To comply with the Zambian legal requirements
To provide a platform to the local people and other Interested and Affected Parties (IAPs)
to suggest how best the mine should operate and how they shall benefit.
To describe the existing environment in terms of ecological resources, physical
environment and socio-economic activities.
To identify major environmental impacts in order to suggest measures to sustain/promote
positive impacts as well as measures for mitigating negative impacts.
To highlight key environmental management costs expected throughout the project life
cycle. recast
4.1.3
COMPONENTS OF THE PROJECT
The proposed project will consist of the following buildings:
Concentrating plant
Ore stockpiles/storage ore
Security camps
Workshop &stores
Offices and accommodation
Smelter plant
4.1.4
NATURE OF THE PROJECT
Rosinvest (Z) Limited Tin project is not complex and the only major activities are Open Pit
Mining, Dewatering and Removal of Overburden Material/Waste Rock. The sub-sections below
briefly describe the major activities of the project. The current and planned activities are both
described.
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The company will be using Open Pit Mining Method using heavy equipment like Excavators,
Bulldozers, Loaders, Drilling Machines and Dump Trucks.
The schedule of activities will be similar to any other mining ventures, starting with mining
which will include ripping of overburden, blasting of the virgin rock and the ore body (vein) and
dumping of the overburden/ waste rock. The extraction of the tin will involve smelting in low
temperature which rises to a maximum height of 300 degrees. There after ore crushing and
washing shall follow. During washing the sorting is done and finally storage of the ore and
disposal of slimes from the washing plant. The storage building will have the capacity of
stocking up to 10,000 metric tons of tin ore.
The process of acquiring tin from its ore will be by the pyro metallurgical smelting methods.
Pyro metallurgical techniques use heat to separate tin from Cassiterite ore, and finally fire and
electrolytic refining. In put materials will be Cassiterite and coal only, oxygen will be pushed
through to the furnace by blower. 60% from the input Cassiterite will come as 98%Tin (Sn), the
impurities will be in the slag.
The company is scheduled to export at least 1000 tons tin ingot 98% Tin to European Countries,
China and the United States of America.
Other scheduled activities are Domestic Waste and Sewage Management, Pit Dewatering,
Domestic Water Supply, Waste Water Management, Fuel Storage, Construction of Fuel Storage
Facilities, Access Roads, Campsite, Security Facility, Mechanical and Metal Fabrication
Workshop, Salvage yard, Magazine, Wash bay, Oil and Water separator etc.
Decommissioning and closure of all these (above mentioned) activities is also part of the
schedule.
These scheduled activities have been discussed in detail in the sections that follow. A life time of
40 years will be the total time in which all these activities will be implemented, starting with
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infrastructure that requires construction, followed by routine activities which are cyclic and
ending with decommissioning and closure activities.
1.1.4.1
OPEN PIT MINING PROCESS AND MINING MACHINERY
Mining activities will be done using open pit mining methods. Major activities will include
removal of overburden material, de-watering activities, defining the pit benches to comply with
standard open pit mining methods and generation of waste rock and overburden material.
The mining equipment that will be used include Excavators, Dump trucks, Compressors, Jack
Hummers, a Water Bowser, a Rock D14 Drilling Machine, Generator and Water Bowser. All
these machines will be hired from local suppliers.
4.1.4.2
MINING DESIGN
The mining plan will start with open pit method for mining, the strike will be to identify the
diameter of the pit and the mining will be on the strike direction, the depth will depend on the ore
vein. The side wall of the pit will be benched 2 meters high. This will be maintained throughout
the mining activities and lifetime of the mine. Entrance to the pit will be through the ramp; one
will be entrance and second will be exit. All mining regulation will be applied in the mining area.
Blasting will be carried out in the hard rock‟s only like quartz and quartzite. No building will be
near to the pit.
To remove all the waste material from the pit, the overburden material will be stripped from the
pit by excavation, controlled blasting will be used for the next level after the OB which is a rock
but highly weathered and the bottom competent layer is blasted using bulk explosives. These
explosives will be stored on site and will be used in accordance with procedures and the license
issued by MSD.
Haulage of the material will be done by using 35 tonnes dump trucks and a single ramp
connecting the surface and the pit bottom that will be used.
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4.1.4.3
ROSINVEST -EIS
OVERBURDEN DUMP (OB)
Waste rock will be managed in areas located at prescribed distances from the proposed open pit.
The placement of waste rock will be initiated with perimeter buttresses designed to minimize the
visual effects of the project for travellers or passers-by and for viewers in the surrounding area.
The outside face of the buttresses will be re-vegetated and reclaimed as they are completed.
Waste rock in the remaining portions of each phase will then be deposited east of (behind) these
buttresses. Waste rock will also be placed in the dry-stack slurry/tailings storage areas to provide
structural and erosional stability of the tailings pile.
4.1.4.3.1
Foundation
Preparation and Stability Portions of the waste rock areas may be required to be cleared and
grubbed of organic materials. Suitable foundation materials will be stockpiled for later use in
reclamation. The remaining alluvial and overburden soils and rocks following clearing and
grubbing (and any foundation stripping) will be considered suitable foundation materials. The
waste rock will be placed with a final safe inter-bench slope. In addition, detailed stability
analyses will be carried out during final design to ensure that the waste rock piles will be stable
during and after placement.
4.1.4.3.2
Waste Rock Facility
Storm water management at the waste rock facilities will be such that for the construction of the
initial perimeter buttresses, concurrent reclamation will progress up the outer slopes as the
buttresses are constructed. They will limit erosion potential while minor diversion channels will
be used to direct runoff to down gradient sediment ponds. Where feasible, the top of the waste
rock facilities will be sloped to facilitate storm water draining towards the open pit.
4.1.4.3.3
Collection and Treatment of Waste Rock Drainage
The waste rock management facilities will be constructed in lifts that will generally not exceed
20m in height. The top surfaces will be constructed with upward gradients of about 0.5% to the
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south-east so that storm water runoff is directed back toward the open pit. The storm water will
be collected along the northern toes of the waste rock facilities and allowed to drain through the
coarse rock along the bottom.
Similarly, surface runoff from the northern faces will be allowed to collect along the toes and
drain through the base of the waste rock storage facilities. This water, along with surface water
runoff from the active face of the waste rock storage area will ultimately be collected in a
sediment pond. This pond will provide sediment control and water catchment for all of the
disturbed areas within the licence area. Runoff and seepage from the waste rock facility will be
sampled and tested for water quality to verify modeling results. The sediment pond will serve as
a final control point for water quality prior to discharge.
Suspended sediments will settle out in the collection pond downstream of the waste rock facility,
and the clarified water will be released.
4.1.4.4
ORE CRUSHING, WASHING PLANT, CONCERTRATOR AND
SMELTER
Rosinvest Zambia Limited shall have a crushing plant, washing plant, concentrator and smelter
at the site. Crushing, screening, and washing and sorting and smelting shall be conducted at the
site.
4.1.4.4.1
CONCENTRATOR DESIGN
The raw material coming from the pit will go straight for screening, followed by primary crusher
then to the secondary crusher screening for classifying the products according to the size. The
product below 2 mm will go direct to jigs, above that will go to crushers. Grinding will be used
when the tin is combined with another mineral like tantalite to separate the two minerals and in
the jig the water will separate them. The amount of water required in this operation will be
calculated and will not be more than 20,000 litres jig/day. (ANNEX 9).
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4.1.4.3.2
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SMELTER DESIGN
The smelting process steps will start with roasting, smelting, converting, and finally fire and
electrolytic. Operation will be carried out by one furnace and one 20x40m storage facility for
stocking approximately 10,000 metric tons containing 70% tin oxide ore in an area about 4,000
m2. (ANNEX 10).
4.1.4.5
DOMESTIC WASTE AND SEWAGE MANAGEMENT
The mine will have a total workforce of 82 and these employees will be staying within the camp.
Meals and other house-keeping services will be provided to employees by the company.
Considering the total workforce at the camp, domestic waste generation is therefore significant.
On the other hand, sewage management is also a significant activity.
The disposal method for domestic waste will be by the use of waste bins that will be provided
and the waste will be disposed of in a land fill located within the license area. The land fill is not
yet established and licensed. The proposed intervention is to have the landfill area licensed with
ZEMA strictly for domestic waste disposal. In order to meet the licensing requirements, one (1)
ha of land will be reserved for the land fill cells. The cells shall be dug in potions and each filled
up cell within a section shall be covered with top soil progressively until it gets full. Top soil in
this regard shall facilitate re-vegetation. Support facilities for the landfill area shall include a
perimeter wire-fence with a lockable gate, warning signs written in English and Tonga and
Nyanja to restrict access and a user instruction notice to remind users to always burry the waste
with top soil.
Regarding sewage management, septic tanks shall be used which will be emptied at regular
intervals. A ZEMA approved Sewerage Company shall be engaged to handle the job.
4.1.4.6
DE-WATERING, DOMESTIC WATER AND WASTE WATER
FACILITIES
Dewatering will be done through in-pit pumping only. About 5000 liters of water is estimated to
be pumped out per day during the rainy season and about 2000 liters per day during the dry
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season. This water will be pumped into a settling pond which will be constructed at the site. The
pumped water shall be used to water the mine to suppress dust. This practice shall continue
throughout the lifetime of the mine. Therefore, no changes are foreseeable unless otherwise.
Domestic water for the camp will be divided in general use and drinking. A borehole will be
sunk by the company for domestic use. Water for general use will be obtained from settling pond
and some from the borehole.
The plan for domestic water is to install a water purifier at the camp for treatment of the aquifer
water for drinking and to sink a borehole within the mine area where domestic water shall be
extracted.
Ultimately, water loss at the mine site will be due to domestic use, dust suppression, seepage,
evaporation and surface flow.
4.1.4.7
FUEL STORAGE FACILITIES
A 20 000 liters diesel storage tank will be installed. The fuel tank will be locally fabricated and
constructed using carbon steel plates (300WA). The ends and the barrels of the tanks will be
fabricated using 6mm thick plates. The tanks shall be pressure tested at 0.7 bars after thoroughly
cleaning it of all loose matter. The tanks will be made in accordance with Zambia Bureau of
Standards as well as meeting the international standards.
The fuel storage tank will be placed 1.5meters from the bund wall. The storage tank will be 6
meters in length and 2.5meters in diameter. The diameters of the inlet and outlet pipes will be
35mm and 20mm respectively. The tanks will have a dip pipe inlet and a vent pipe outlet and
will be fitted with a ladder with handrails.
4.1.4.8
MINE SITE ACCESS ROAD
Rosinvest Zambia Limited will develop two access roads connecting to the site. One will be for
the public and the other one for the mine equipment.
The access roads shall periodically be maintained by re-surfacing them with gravel and filling all
the depressed points. Maintenance facilities that shall be installed shall include spoon drains and
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culverts at appropriate places. In addition, the access road for mining equipment shall be
widened to about 4.5 meters width to facilitate safe and smooth movement of the 35 tonnes
trucks and the dust suppression water bowser.
In order to ensure good safety to other road users, all necessary traffic signs shall be installed
along the access roads.
4.1.4.9
ACCOMMODATION AND SECURITY FACILITIES
The mine camp will have a perimeter wire fence covering a footprint of 2.0 hectares. All
accommodation facilities will be located within the wire-fence. The accommodation
infrastructure at the camp will be a combination of accommodation containers and hostels made
of concrete blocks.
There will 7 hostels, the Director‟s House, the Mine Manager‟s House and the Security
Manager‟s House. Other facilities will include a strong room, kitchen, guard house, generator
shelter, ablution blocks and containerized offices. The camp is currently serviced by two septic
tanks.
4.1.4.10
MECHANICAL AND METAL FABRICATION WORKSHOP
The hired mining machines and light vehicles will be serviced at the site. In order to comply with
legal requirements for management of hazardous waste, a standard workshop shall be
constructed. The workshop shall have all the required facilities for generation and storage of
hazardous waste including storage of hazardous waste from the camp. Warning signs shall also
be installed to educate workers about the hazardous nature of waste that shall be generated from
the camp.
Key sections for the workshop shall include a bunded storage section with concrete lining and
partitioned to restrict access. This shall be used for storage of all the hazardous waste that shall
be generated from the mine site. The workshop shall have a concrete lined service bay for heavy
machines and another section for light vehicles. A perimeter drain shall be constructed to
connect both service areas to an oil/water separator. Used oil and used batteries shall be collected
from site for re-use and recycling respectively by licensed companies. Healthcare waste shall be
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transported to the nearby Healthy Clinic for appropriate disposal. The remaining hazardous
waste specifically used oil filters and used fluorescent tubes shall be dumped at the nearest
ZEMA licensed dumpsite and in an event that such a facility shall not be found, the waste shall
be kept within the hazardous waste storage facility at the camp awaiting disposal at the right
facility.
A small metal fabrication workshop shall also be included as part of the main workshop. The
only waste from this section shall be metal off-cuts and swarf. The swarf shall be treated as
hazardous waste whereas metal off-cuts shall be kept for alternative uses.
4.1.4.11
SALVAGE YARD
Scrap material will be generated and this is expected to continue. Lack of a good management
system for scrap material can lead to poor housekeeping. This may consequently become a
hazard to human health and the environment. Within the camp perimeter fence, a small section
of 60 meters by 80 meters shall be dedicated for storage of scrap material. This shall be
partitioned with a wire fence and all the scrap material shall systematically be kept under lock
and key. The Security Manager shall be responsible for the salvage yard and once in a while, the
scrap material shall be disposed off.
4.1.4.12
EXPLOSIVES STORAGE FACILITIES
The proposed plan is to construct the Explosives Magazine. The position of the Magazine will be
about 500m further north east the camp and the mining pit. Since explosives storage and use is
regulated by MSD, all the necessary permits will be obtained and the Magazine will be
constructed in accordance with prescribed standards.
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Fig 11:
4.1.4.12.1
ROSINVEST -EIS
Mine Lay out showing an Explosives Magazine
Risk Assessment
Rosinvest will appoint one or more Safety Officer(s) who will assist in supporting a tactical plan
to address risks so they can be eliminated or be reduced to an acceptable level.
A safety decision-making model will be used to brief Safety Officers regarding the nature of the
incident, the allocated task and prevailing hazards and risks. The Incident Commander will
confirm that the Safety Officer understands:
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their role and area of responsibility
allocated tasks
Lines of communication.
The Safety Officer will:
be competent to perform the role
ensure personnel are wearing appropriate personal protective equipment
monitor the physical condition of personnel and/or general or specific safety conditions at
the incident, in accordance with their brief
take any urgent corrective action required to ensure safety of personnel
update the Incident Commander or senior safety officer regarding any change in
circumstances
Not be engaged in any other aspect of operations, unless this is required to deal with a
risk critical situation.
The activities of a Safety Officer will be carried out by any of the Explosives and Rescue Service
roles, but the complexity of the task, size of the incident and scope of responsibility will be
considered by the Incident Commander when determining the supervisory level required.
4.1.4.12.2
Response Plans
There should be in place response plans for all locations where explosives maybe found
including „temporary arrangements‟ for instance during loading/unloading of explosives on site.
The plans will be a mixture of those required by legislation and the Explosives and Rescue
Service‟s tactical plan.
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4.1.4.12.3
ROSINVEST -EIS
Storage
The explosives will be typically held in a steel store, the site will also have a detonator annexe.
Most of the explosives will be mixed on-site from non-explosive ingredients. The contents of the
storage facility will be correctly identified through the use of hazard placards.
The Magazine will have a buffer zone of 700 m radius. It will be constructed to meet all
applicable fire code and mining industry safety standards, and will be accessible only to
authorized personnel.
4.1.4.13
DUST SUPPRESSION FACILITIES
A water bowser with a carrying capacity of 10,000 liters will be used to suppress dust at the
mine. This facility will be used for dust suppression along the haulage roads from the pit to the
OB dump and the service is extended to the public route connecting Rosinvest Zambia Limited
mine. The bowser shall be available for throughout the mine life.
In addition to the water bowser, water sprays using horse pipes shall be introduced and this
activity shall be conducted as part of good house-keeping.
The water that shall be used for dust suppression shall be pumped from the open pit as part of
dewatering or it shall be pumped from the settling pond.
4.1.4.14
HEAVY MACHINES AND LIGHT VEHICLE WASHING BAY
A washing bay for heavy machines and light vehicles shall be constructed next to the workshop.
To accommodate big dump trucks, the wash-bay shall be 50m by 50m in size. It shall be
concrete lined with a concrete lined perimeter drain which shall direct all the effluent into a silt
trap. The silt trap shall also be concrete lined.
After trapping solids in the silt trap, the overflow shall be directed through another concrete lined
drain into the workshop‟s oil/water separator. Alternatively, the wash-bay will have its own
oil/water separator to avoid overload of the workshop oil/water separator. Effluent from the
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oil/water separator shall be directed into a soak-away and this effluent shall be monitored for
total hydrocarbons as proposed in the Monitoring Plan.
4.2
DESCRIPTION OF THE PROJECT LIFECYCLE ACTIVITIES
Three phases shall be applied to develop Rosinvest Mining for the life span of 40 years. These
will include;
4.2.1 Construction Phase
This phase shall include the following:
Infrastructure development which shall involve vegetation clearing to establish Base
Camps from where the work teams will be operating and the opening up of the forest
area through developing access roads
Construction of an explosives magazine to an appropriate site taking into account the safe
distance. This involves site clearing, leveling and construction activities and it is being
done in consultation with MSD who are the supreme regulator for such mining facilities.
Construction of a standard workshop.
Construction of Crushing and Washing plants
Installation of the Smelter and concentrator
Construction of a fuel bowser packing bay.
Installation of a modular sewage treatment facility.
Sinking of a domestic water borehole.
Construction of an OB
Construction of perimeter drains/silt traps for the overburden dump.
Construction of a Crusher/Screening and Smelter Plant
Installation of drinking water treatment equipment (filter).
Installation of a Generator
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4.2.2 Operation Phase
4.2.2.1
Mining Phase
Open pit operations will mainly comprise of drilling, controlled blasting, excavation, loading
and hauling. The overburden and waste rock material generated will be dumped at the waste
rock dump sites. Some waste rock generated from the operations of the mine will be used for
the construction of the access roads in the area.
4.2.2.2 Production Sequence
Open Pit/Cast or surface mining will be the mining method to be used at Rosinvest mine due
to the position of potential ore bodies which are near the land surface. The ultimate extent of
the pit will be based on long-range price forecasts for ore as well as engineering estimates of
operating costs, processing plant recoveries, charges, and marketing payment terms. The
design of the open pit and internal mining phases will incorporate geotechnical
recommendations for safe slope angles, internal ramp development for access to all working
areas, and pit wall smoothing to enhance stability and operator safety. Pit slope angles
between ramps will vary according to rock strength, lithology and structural controls, but are
expected to range between 28° and 48° between ramps. Where possible, catch benches will be
spaced on approximately 30m vertical intervals to maximize the effective widths.
ROSINVEST will ensure that the optimum extraction grade and quality is planned to remain
“at best” relatively constant throughout the extraction process. Principally, the walls of the
mine will be dug out in steps called benches that will provide a safe stable structure to the pit
walls, and also will allow earth moving machinery to have access when expanding the size of
the pit. In order to expand the size of the pit or to excavate in any certain direction, the rock
will be removed nearest the top of the pit, working sideways before moving down to the next
bench thus obtaining a safe angle of the pit walls at all times. Before the rock can be removed,
it will be broken up into manageable pieces. This will be done by drilling strategic holes into
the rock, which will be then filled with explosives. Consideration of the location and depth of
the holes will be very important as to fracture the rock in a way that will allow the shape of
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the pit to remain constant, prior to any detonation of explosives. Around the pit will be a
declining road or haul road to be cut into the walls of the pit that will allow large earth
moving machinery and vehicles access to the bottom of the pit floor. The benches will be
arranged as steps, with berms and the batter.
The mining design is of critical importance to the operations and therefore ROSINVEST shall
ensure that excavation at reasonable distance is started in order to have safe mining practices
and be able to maintain the natural angle of repose.
4.2.2.3 Mine Equipment
Machinery to be used will include but not limited to mechanized equipment such as drilling
machines, compressors, water pumps, generators, excavators and bulldozers, etc.
ROSINVEST will also use dump trucks, and any other heavy duty equipment to be
recommended by mining engineers.
The final equipment selection and fleet sizes may vary slightly with vendor selection and
future mine optimization studies. Production blast-hole drilling will be performed by dieseland/or electrically powered rotary rigs. A diesel powered percussion drill (12mm to 15mm
diameter holes) will be used for haul road and bench pioneering work and secondary rock
breakage. Electrically-powered mining shovels with will perform the bulk of the ore and
waste rock loading. Two front-end loaders will augment the shovel fleet and be used for
safety berm maintenance, bench pioneering, road construction, bench toe clean-up, and
constructing pit-bottom sumps.
Off-highway trucks will be used for the production haulage of all ore and waste rock. These
will be diesel powered units with either mechanical or electrical drive systems. The final truck
selection will be based on manufacturers' supply capabilities, tire availability, and economic
considerations. A computer – based truck dispatch system may be employed to direct haul
trucks to available loading units, maximize unit truck productivities, and maintain production
and performance records of the mine operations. This might require the use of a high
bandwidth radio communication system for data transfer between mobile units and the
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computer base station. An electric power line will be constructed around the perimeter of the
pit to supply energy to the shovels, pit dewatering systems and, potentially, to a trolley-assist
system for the haul trucks. Radial power lines will extend down into the pit to substations
located near the working faces.
Large (580- to 850-hp) crawler dozers will be used for road and sump construction, clearing
benches, trimming pit wall faces and maintaining the waste rock storage area, re-grading
waste rock storage area slopes for reclamation, and other tasks in and around the mine.
Rubber-tired dozers (630-hp) will be used primarily for cleaning up the shovel area, patrolling
the road, and clearing of blast hole sites. Motor graders (270- to 500-hp) will be used for
constructing and maintaining roads throughout the Project area. The 270- hp grader will also
be used for maintaining the project access road from SR 83 to the plant site. Water trucks,
with tank capacities of up to 110,000 Litres each, will be used to control dust emissions from
the mine haul roads. Road water for pit haul roads will be taken from the pit dewatering
system or the process water temporary storage (PWTS) pond located near the plant site.
Temporary holding tanks will be used for some limited storage and to fill water trucks close
to the main haul roads. Roads external to the pit will be watered using fresh water. Separate
water stands and holding tanks will be maintained for this purpose. In addition to the major
mining equipment described above ROSINVEST mine operations and maintenance crews will
require other support equipment, including, but not limited to, explosive blasting agent
delivery trucks, an 8-cy front-end loader, 25- T haul trucks (for stemming deliveries and
spreading aggregate), backhoe/loaders, a portable aggregate crushing and screening plant
(brought in periodically by a contractor to produce stemming and road surfacing material), an
all-terrain and weather crane, fuel/lube trucks, mechanic field service trucks, a 200- T
transporter/trailer, a tire handling truck, integrated tool carriers, forklifts, light plants, pickup
trucks and crew vans, etc.
The summarised operational phase as explained above shall include the following:
Removal of the mining waste to access the Tin mineralized ore;
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Mining/ extracting the Tin ore and transporting the ore material to Crushing and Washing
Plant.
Concentrating and Smelting of the Tin ore
Maintenance of all support facilities that shall be constructed;
Generation and disposal of waste rock and overburden;
Dewatering activities;
Dust suppression activities;
Progressive backfilling of the pit with waste rock once the vain is accessed;
Generation of domestic waste and hazardous waste; and
Environmental Management
Transportation of diesel to the mine, storage and use.
4.2.3
Decommissioning Phase
The phase shall include the following:
Stabilizing the open pit to ensure that it remains physically stable.
Environmental monitoring activities and submission of necessary statutory report about
decommissioning and closures activities.
Stabilizing the overburden dump and re-vegetating sections where overburden material
shall be dumped.
Repairing all the structures to a suitable state for alternative uses.
Rehabilitating all contaminated sites such as the workshop area and the surrounding for
the fuel storage facility.
Installation of necessary warning signs around the pit and dump sites
Conducting re-vegetation activities where possible.
4.3
PROJECT INPUTS AND OUTPUTS
Based on the activities listed above, an input-output analyses was done to facilitate understand
possible impacts. The table below presents these inputs and outputs.
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Table 7 Project Inputs and Outputs
INPUTS
Fuel
POSITIVE OUTPUTS
NEGATIVE OUTPUT
Powering mining machines.
Powering
the
generator
for
electricity.
Transportation of water and raw
Soil, ground water and
surface water
Contamination due to leakages.
Safety hazards
material
Lubricants
Smooth operations of machines
Generation of hazardous waste
Other mobile
Smooth operation of machines
Generation of
hazardous waste
equipment
consumables (batteries,
Filters, tires etc.)
Labor
Mining machinery
N/A
Mining activities
Income to employees
Multiplier economic effects
Production of Tin
Vibration
Transportation of waste and Tin Hazardous waste generation
Generation of used tires
ore
Generation of scrap metal
Mining activities
Production of Tin
Generation of overburden
Generation of effluent
Dust generation.
Land degradation
Light vehicles
Transportation of employees
Transportation of consumables
Generation of hazardous waste
Generation of used tires and
other related scrap.
Accommodation
Shelter to employees
facilities
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Food for workers
Nutrition supplement to workers
Domestic waste Generation
Explosives
Facilitate mining activities
Noise and vibration
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5.0 PROJECT ALTERNATIVES
A variety of alternatives, such as the following, exist for the design and management of the
project:
5. 1
NO PROJECT, AVOID OR POSTPONE ALTERNATIVE
Avoid or postpone the need for the proposed development altogether. Under the do-nothing
alternative, there will be no possibility to have the much needed mining development at the
proposed site. The do-nothing alternative will impact economic development and might hinder
developer efforts of mining at the proposed site. Without the implementation of the project, the
government and other relevant stakeholders in the project cycle would continually have
shortages which can improve the livelihood of the local people and government revenue. This
would deprive them the opportunity for benefits to enhance development of the District. The
„Do Nothing‟ option is clearly not advisable given the heavy socio-economic costs it would
entail.
5. 2
SITE ALTERNATIVES
No site alternatives were considered for the project as the proposed site was identified as being
suitable for the project. The site is located in a geologically surveyed area and mapped by
Ministry of Mines and deemed to contain mineral reserves. With the vast development in the
country the project and as such the site was considered viable. The site was specifically chosen
due to the occurrence of Tin deposits in the area.
The advantages of the specific site are as follows:
The site is easily accessible.
Availability of labor.
Location of the project site is convenient for the mining.
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5.3
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MINING METHODS
Two options were considered. That is, open pit mining and underground mining methods.
Considering the depth of the mineralized material, it is not feasible to undertake underground
mining. The mineral resources are not anticipated to go beyond 200 meters deep and this top
section of the earth is highly weathered making underground mining very dangerous.
5.4
ORE PROCESSING
Smelting is a form of extractive metallurgy; its main use is to produce a metal from its ore. This
includes production of tin and other base metals from their ores. Smelting uses heat and
chemical reducing agent to decompose the ore, carbon ore such as coke, or in earlier time
charcoal. Tin production through smelting will follow the process outlined below:
5.4.1
Process
Smelting involves more than just melting out of its ore. Tin is a chemical compound of the
metal with other elements, such as oxygen (SnO2. To produce the metal Tin, these compounds
have to undergo a chemical reaction. Smelting therefore consist of using suitable reducing
substances that will combine with those oxidizing elements to free the metal. This process
follows the chemical process as shown below:
SnO2 →Sn + O2
5.5
HIRING OF MINING MACHINES AGAINST BUYING THE MACHINES
Two options were considered. These are buying the mining machines and hiring. Buying
machines was found economical than hiring considering the life of the mine which is
anticipated to last for about 40 years.
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5.6
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MINING WASTE DISPOSAL ALTERNATIVES
Developing a new overburden dumps and waste rock dumps was preferred since it is a new
development.
5.7
CONSTRUCTION OF THE WASHING PLANT AND CRUSHER
Construction of a washing plant and crushing plant at the site was considered since it is a new
development.
5.8
POWER SUPPLY ALTERNATIVES
A diesel powered generator was considered against connecting the site to the national hydro
power supply line. Cost limitations made the use of a diesel powered generation to be the
preferred alternative. Therefore, a power line connecting the site to the national hydroelectricity line shall not be done because of the cost and distance where the national hydro
power supply is (167km) from the site. It has been estimated that a 250litres of Diesel will be
used per day to power the plant and the mine. A 20,000litre surface tank made from mild steel
and supplied by Mount Meru Fuel Services shall be installed to feed diesel fuel to the generator.
5.9
FUEL STORAGE ALTERNATIVES
Construction of an above ground diesel storage tanks at the site was considered against use of a
diesel bowser to transport diesel. The first option was adopted due to cost limitations
considering the distance from the CBD (Kalomo) to the site. (ANNEX 16).
A 20 000 liters diesel storage tank will be installed. The fuel tank will be locally fabricated and
constructed using carbon steel plates (300WA). The ends and the barrels of the tanks will be
fabricated using 6mm thick plates. The tanks shall be pressure tested at 0.7 bars after thoroughly
cleaning it of all loose matter.
The fuel storage tank will be placed 1.5meters from the bund wall. The storage tank will be 6
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meters in length and 2.5meters in diameter. The diameters of the inlet and outlet pipes will be
35mm and 20mm respectively. The tank will have a dip pipe inlet and a vent pipe outlet and will
be fitted with a ladder with handrails.
5.10
DOMESTIC WASTE DISPOSAL FACILITIES
The first alternative was to have the waste collected in bins for disposal at the nearest licensed
disposal facility. The nearest dumpsite in this case is in Kalomo District. Transportation costs
limited this option. Therefore, creating a dumpsite at the mine which would then be licensed for
domestic waste disposal was the most practical. This dumpsite shall only be used for domestic
waste disposal.
5.11 SEWAGE MANAGEMENT
The use of Pit latrine was evaluated against the use of Septic Tanks or installing a Mini
Sewerage Treatment Plant. Pit Latrine has their own limitations and is not very good for a huge
number of people. There are also legal demands to avoid use of Pit Latrine in Zambia.
Therefore, the use of Septic Tanks or installing a Mini Sewerage Treatment Plant was preferred.
5.12 “WITHOUT PROJECT” ALTERNATIVE”
The alternative of not implementing the project was rejected by the proponent for the following
reasons;
The developer would like to contribute to local, regional economic growth through
mining of tin ore which may be found at the proposed site.
By not undertaking the proposed project local community will lose out the social
responsibility package the developer intends to initiate as a way of helping the local
people facing the challenges of poverty.
The company may have loss of business from the intended buyers of Tin.
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Not undertaking the proposed project will mean loss of business for various firms that
will be engaged by the company to supply goods and services to use at the proposed
project site.
There will be loss of sources of livelihood for families of would-be skilled and unskilled
employees at the proposed project site.
Both central and local government will lose direct and indirect revenue collected
through various taxes and levies respectively and
By not undertaking the proposed project, the much needed growth of Zambian economy
will be hampered.
5.13 PROCESS AND MATERIALS
The proposed
mining processes,
equipment
and materials
are
all
environmentally
sustainable and hence unlikely to cause any major damages to the environment. Rubble remains
during construction will be used for compaction and site leveling, while solid and sewer waste
will be managed by the proponent by use of waste bins and septic tanks.
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6.0
ENVIRONMENTAL AND SOCIAL MANAGEMENT PLANS
6.1
OBJECTIVE
The objectives of the EMP are to provide:
The Project Management Team with evidence of practical and achievable plans to ensure
that the project‟s environmental requirements are complied with.
An integrated plan for monitoring, assessing and controlling potential impacts;
Local, Regional and National authorities with a framework to confirm compliance with
policies and requirements; and
The community with evidence that the Rosinvest Mine Project will be managed in an
environmentally acceptable manner.
The detailed EMP will be reviewed and periodically updated, if necessary to reflect knowledge
gained during the course of the project‟s construction and operations. Changes to the detailed
EMP will be implemented in consultation with the relevant authorities where necessary.
6.2
LEGISLATION, COMPANY POLICIES AND LIMITATIONS
In accordance with Zambian EIA Regulation S.I. No. 28 and the IFC Performance Standards,
ROSINVEST is required to present an Environmental & Social Management (ESMP) to reduce
or offset and/or eliminate any impacts that have been identified as significant. ROSINVEST will
be responsible for implementing the ESMP, which will include the actions, and associated costs,
of the mitigation and rehabilitation program.
The Environmental & Social Management Plan for the project is well defined and considers the
environmental and social impacts of the entire operation lifecycle (including exploration and
planning, evaluation, operation and closure) in addition to occupational health and safety
management, describing both mitigation and management measures that are recommended for
important functions at various stages throughout the mine life.
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ROSINVEST will prescribe all the mitigation and rehabilitation measures for each of the
identified activities or operation which may lead to significant impacts during each phase of the
project.
This EMP is based on the application of professional judgment to certain facts with resultant
subjective interpretations. Professional judgments expressed herein are based on the facts
currently available within the limits of the scope of work, information provided by the client or
its representative, prevailing secondary data, budget and schedule. To the extent that more
definitive conclusions are desired by the client than are warranted by the currently available
facts, it is specifically Tropical Environmental Management Experts‟s intent that the conclusions
and recommendations stated herein will be intended as guidance and not necessarily a firm
course of action except where explicitly stated as such. We make no warranties, expressed or
implied, including, without limitation, warranties as to merchantability or fitness for a particular
purpose.
The ESMP is subdivided into sections as appropriate. The plan specifies:
What needs to be managed? (Environmental Issue)
Why does it need to be managed? (Environmental Impact)
How should it be managed? (Management Action)
Who should manage it? (Responsibility)
By when should it be managed? (Timeline)
What tells whether or not it is managed? (Performance indicators) In this report
The ESMP is structured to facilitate environmental auditing of operations. The management
actions proposed to mitigate the project impacts are based on industrial best practice and the
Zambian regulatory framework.
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6.3
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PRE-MINING PHASE IMPACTS AND MITIGATIONS
6.3.1 Introduction
This section describes these potential environmental impacts and recommends management and
mitigation measures during the pre-mining phase of the Project.
Production and auxiliary facilities to be constructed will include; mining production area: open
pits, vehicle repair workshops, mine offices, mine camp and an electric substation;
Ore crushing facilities: primary crushing to facilitate transfer to the processing plant;
Processing plant;
Tailings storage facility;
Waste disposal areas;
Mine roads; and
Water pipeline and water tanks;
These production and auxiliary facilities will be used for the life of the mine. In addition, some
temporary facilities will be developed for the pre-mining phase only, such as storage areas for
construction materials and construction machinery parking area.
The majority of the impacts identified for the pre-mining phase tend to fall in the moderate
category in terms of consequence and are likely to occur. However, the mitigation measures
outlined explain how these impacts can be reduced to acceptable levels.
Construction will have impact on the visual character and landscape in the Project area. There
will change land-use in the area. Any encroachment on Chilobe and Chana streams in the area
will be avoided. A Closure and Rehabilitation Plan and the Social Management Plan will be
required to manage these impacts to tolerable levels up to mine closure.
There are no likely or very likely catastrophic impacts during the Project construction phase.
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An Environmental & Social Management Plan (ESMP) has been developed which incorporates
the findings of this EIS into a series of categories for implementation.
6.3.2 Summary of the Environmental Impacts – Pre-Mining Phase
A summary of the environmental impacts during the pre-mining phase are listed in Table below.
Table 8
Environmental Impacts Pre-Mining Phase
NO. Potential Impact
Source
1
Removal of vegetation from construction sites
Landscape & Visual Character(EC1)
Landscape re-profiling for construction process
Construction of surface infrastructure
2
Soil
Loss of soil productivity due to topsoil &
vegetation removal Accidental oil / fuel /
chemical / reagent spills Contamination from
fugitive dust emissions Increased erosion due to
vegetation removal Contamination from waste
material e.g. scrap metal
3
Land Use
Change of some areas from agriculture to mining
activities
4
Air Quality
Construction equipment and vehicles exhaust
emissions and dust generation
Fugitive
dust
emissions
from
mine
construction
5
Noise / Vibration
Construction equipment and vehicles
Mine Site facility construction and operation
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6
Surface Water
Change
in
drainage
ROSINVEST -EIS
topography
due
to
construction Clearance of riparian vegetation may
affect the hydrological regime locally
Siltation in water courses due to increased soil
erosion from removal of vegetation
Fugitive dust emissions may contaminate water
Courses Domestic Waste Water Discharge
Mine Water Discharge Accidental oil / fuel /
chemical / reagent spillages
7
Ground Water
Contamination from accidental spills and oil
infiltrating from surface water
8
Ecological Environment
Loss of habitat due to vegetation removal
Habitat disturbance due to construction vehicles
and plant machinery
Increased fugitive dust will reduce biological
activity Accidental oil / fuel / chemical
Increased hunting and poaching
9
Cultural Heritage / Archaeology
Damage to cultural sites
Damage to archaeological relics
10
Solid Waste
Damage to the physical and social environment
11
Customary Land
Conversion of customary land previous utilised
by the community to a mining licence area
6.3.3 Pre-Mining Impacts Mitigation and Management
6.3.3.1
Landscape and Visual Character
Cause and Comment
The main components of visual intrusion to receptors around the Project site will be the waste
rock dumps and Tailings Storage Facilities. The area is a Greenfield site and there is potential of
loss of scenic integrity of the area.
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Significance of Impact
Consequence
Probability
Major
Very likely
Mitigation Measures
The following mitigation measures will be carried out to reduce the impact significance:
Avoiding removal of vegetation as well as encouraging re-vegetation around the mine
facilities;
Avoid stockpiling the ore at the mine;
Revegetation programs will be implemented during the course of the pre-mining phase.
Areas that have been exposed during construction e.g. road cuttings and drainage ditches
will be re-vegetated to avoid undue visual impacts; and
Normal or non-reflective paints and tones that blend with the infrastructure in the area
will be used in the finishes on the plant and other buildings, where practically possible.
Therefore, mitigation will enhance the shielding of the mining facilities from the communities.
Impact Classification
The impact on visual aesthetics will be direct and irreversible.
Effectiveness of the proposed measures
The proposed measures are likely to be 98% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
Life Span of the Project
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6.3.3.2
ROSINVEST -EIS
Soils
Cause and Comment
The pre-mining and mining phases will most likely reduce the agricultural potential of the soils
as well as the land capabilities of the project site. Soil erosion in the rain season is expected to
increase after clearing the site. There may also be accidental fuel and oil spillages within the
surroundings.
Significance of Impact
Consequence
Probability
Moderate
Likely
Mitigation Measures
Restrict clearing to areas essential for mining;
Before construction of the mine camp, workshop, offices and other surface infrastructure,
top soil will be stripped and stockpiled. This material will be used for rehabilitation at
mine closure;
Vehicles and other mine machinery will only use maintained tracks and roads;
Hydrocarbons to be used at the mine will be stored and handled in the heavy equipment
workshop to lined with impermeable surfaces, oil traps and bunded;
At utmost prevent or institute an emergency clean-up of spillage or leakage of hazardous
material or any hydrocarbons from mining equipment or vehicles immediately it occurs;
Potentially contaminated runoff from the equipment workshop and light vehicle car park
area will be directed to the settlement ponds. The sludge will be taken for
decontamination at the bioremediation facility to be located within the mine licence;
Storm water and runoff from upstream catchments will be diverted away from active
mining and disturbed areas by bund walls to be erected around the facilities. Run-off
from these facilities will be contained by these same walls;
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Areas in the project area awaiting rehabilitation will be lower than surrounding landform,
which effectively provides internally draining sumps that contain storm water runoff and
run-off will be cleared from these areas immediately after the rain event;
Areas disturbed by mining activities and infrastructure are to be rehabilitated to a stable
landform with a self-sustaining vegetation cover and where possible post mining drainage
flows will emulate pre mining flows;
Disturbed areas around construction sites will be rehabilitated promptly;
Sediment traps will be included as part of the drainage designs at points where haul roads
cross watercourses or channels; and
Fuel storage areas have the potential to cause land contamination through leaks, spills and
rupture of tanks. ROSINVEST has elected not to have any fuel storage tank belowground but above-ground for easy management and monitoring. Tanks will have
containments both on the surface and side walls.
Impact Classification
The negative impact on soils will be cumulative and irreversible.
Effectiveness of the proposed measures
The proposed measures are likely to be 95% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
Life of the Project.
The management measures for pre-mining activities within the Project area including access
roads outside of the mining perimeter are presented in summary in Table 6-6.
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6.3.3.3
ROSINVEST -EIS
Land Use
Cause and Comment
The construction phase will most likely change the land use in the area. Land use conflict is not
expected as the project will be implemented within the license area and away from settlements.
However, some fields will be affected. Rosinvest will meet the affected people and offer
alternative land located in safe areas within its mining licence. It will also help affected people
clear these fields.
Significance of Impact
Consequence
Probability
Minor
Likely
Construction in the area may effect change from vegetated areas to mining activities.
Effectiveness of the proposed measure
The proposed measure is likely to be 100% effective.
Duration:
6.3.3.4
Life of the Project.
Air Quality and Atmospheric Emissions
Cause and Comment
It is estimated that during the pre-mining and mining phases, ambient dust and exhaust fumes
levels in the vicinity of the project are expected to increase due to the use of earth moving
equipment and blasting activities. Excavation and Hauling machinery are expected to generate
dust and exhaust fumes. No dust and exhaust fumes are expected at post mining phase
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Receptors of dust and exhaust fumes coming from the construction works will be the workers on
site, people living along the access routes and people walking in nearby footpaths. The impact
will be more significant for the workers and people living along access routes.
Significance of Impact
Consequence
Probability
Moderate
Likely
The potential sources of air emissions during construction are:
Mine sites and roads; and
Exhaust fumes from the operation of construction vehicles and heavy mining equipment
Air Emissions Management and Mitigations
PM10 dust levels are expected to remain below the Zambian guideline levels during the
life of mine.
ROSINVEST will still implement dust suppression measures to control any dust that may
be generated. Good practice will involve implementation of the following dust
management measures to minimize health impacts:
Keeping of on-site and haulage roads moist using water sprayers especially during the
dry season. Alternatively, the application of a dusticide or molasses will be considered;
Implementation of the workplace health and safety plan that addresses health impacts of
dust; and
Providing approved personal protective equipment to the people working in dust prone
areas.
Impact Classification
The impact on air quality will be direct and reversible.
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Effectiveness of the proposed measures
The proposed measures are likely to be 95% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
Life of the Project.
The management measures for construction activities within the Project area and implementation
of mitigation measures for air-emission reduction are presented in summary in Table 6-4.
6.3.3.5
Noise and Vibrations
Cause and Comment – Noise
The sources of noise may vary according to daily activities. The major sources of noise during
construction phase will mainly be earth moving equipment, drilling and blasting activities. The
other major potential noise sources are transportation of personnel, materials, ore and waste rock.
Much of these activities will occur 24 hours a day, the impact of which will be felt most severely
at night when meteorological conditions favour noise propagation.
Significance of Impact
Consequence
Probability
Moderate
Likely
Continuous and permanent noise will be present in the various working areas of the construction
site e.g. open pits, processing plant and on WRDs etc. Some of the control measures are as
follow:
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Engineering controls; Engineering controls modify the equipment or the work area to
make it quieter. Examples of engineering controls are: substituting existing equipment
with quieter equipment; retro-fitting existing equipment with damping materials,
mufflers, or enclosures; erecting barriers; and maintenance. Simple maintenance can
reduce noise by 50%.
Administrative Controls; these are management decisions on work activities, work
rotation and work load to reduce workers‟ exposure to high noise levels. Typical
management decisions that reduce worker exposures to noise are: moving workers away
from the noise source; restricting access to areas; rotating workers performing noisy
tasks; and shutting down noisy equipment when not needed; Noisy equipment can be
sited as far away as possible from workers and residents; and
Personal Protective Equipment; Earplugs are the typical PPE given to workers to reduce
their exposure to noise. Earplugs are the control of last resort and should only be
provided when other means of noise controls are infeasible. As a general rule, workers
should be using earplugs whenever they are exposed to noise levels of 70 dB (A) or when
they have to shout in order to communicate.
Noise Monitoring Program
Rosinvest will implement a monthly noise monitoring program to ensure compliance with the
stipulated IFC noise guidelines. Site-specific monitoring will be conducted at strategic points
(areas likely to exceed 70dBA and 55dBA [during the day] and 70dBA and 45dBA [at night]
within the mine site and in the communities) when construction begins. All areas that exceed or
are within 10dB of the limit will be designated as noisy areas.
These areas will be demarcated and sign-posted.
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Cause and Comment – Vibrations
The blasting and movements of machinery will likely induce ground vibrations around the
project and surrounding areas. Vibrations have the potential to induce cracking of structures and
cause annoyance to the local people.
Significance of Impact
Consequence
Probability
Moderate
Likely
Mitigation Measures
Monitor vibration due to mining activities at the open pits in order to determine any
adverse effects on facilities near the mine site such as the tailing dam and waste rock
dumps;
Traffic vibrations and noise should be managed by ensuring smooth roadways as far as it
is practicable; and
Blast vibration information will be monitored for every blast and evaluated periodically
to ensure that all the blast generated vibrations and acoustic parameters fall within the
desired limits.
In terms of vibration management, Rosinvest Mine Project operations will not emit vibrations at
ground level higher than 1.25cm/s or air pressures greater than 120 linear decibels.
Effectiveness of the proposed measures
The proposed measures are likely to be 95% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
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Impact Classification
The impact of vibration will be direct and reversible.
Duration:
6.3.3.6
Life of the Project.
Surface Water
Cause and Comment
Clearing of surrounding areas in the project area will likely cause siltation, especially during
rainfall events, the runoff around the project site and haulage road, may eventually find its way
into the nearby Chilobe and Chana streams.
Reducing the impact of such a discharge is reliant on sound design and good housekeeping
measures being maintained throughout the life of the mine. Effective monitoring is necessary to
ensure that any impact is rapidly identified so that it can be addressed.
Significance of Impact
Consequence
Probability
Major Impact
Unlikely
The potential significant impacts on surface water sources are:
Landscaping and the clearance of vegetation can affect the hydrological regime locally
due to increased erosion and siltation in water courses;
Soil scouring during floods following site-clearing for the construction of surface
infrastructure and widening of the haul road may lead to increased suspended solids in
the surface run-off; and
Fugitive dust emissions can contaminate water courses.
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The following mitigation measures will be carried out to minimize risks of surface and ground
water contamination during high rainfall periods:
A perimeter drain will be constructed around the WRDs, TSF and ore handling facilities
to control potential water contamination. All the water will be collected in the wastewater
ponds to be located near the potential polluting sites and released to the environment
when declared safe;
Surface water will continue to be monitored for pollution levels; and
Rosinvest will clean any oil and diesel spills as soon as possible.
Impact Classification
The impact on surface water will be direct and reversible.
Effectiveness of the proposed measures
The proposed measures are likely to be 95% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
Life of the Project.
Ground Water
Cause and Comment
A Hydrogeological regime of the area indicated that the area has potential aquifers. This is as a
result of the presence of favourable hydrogeology and presence of absence of fractures within the
rocks.
Significance of Impact
Consequence
Probability
Minor
Unlikely
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Mitigation Measures
The following mitigation measures are recommended to minimize risks of ground water
contamination during high rainfall periods:
Before commencing mining operations, Rosinvest will sink boreholes for monitoring the
quantity and quality of groundwater around the mine;
Results of the quantities and quality of water will be submitted to ZEMA and MSD on
quarterly basis;
All potential polluting sources will be lined with impermeable surfaces; and
Rosinvest will minimise any spillages of oils, waste material and any other chemical
spills that can contaminate groundwater.
Impact Classification
The impact on ground water will be direct and reversible.
Effectiveness of the proposed measures
The proposed measures are likely to be 95% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
6.3.3.7
Life of the Project
Ecological Environment
Cause and Comment
The biodiversity assessment indicated that the project site has good biodiversity. It is an
Important Bird Area. The project area has the potential of impacting negative on this
environment. If not properly managed, the project can also lead to the degradation of terrestrial
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and aquatic ecosystems. The destruction and disturbance is expected to be more on the footprint
of the Area of Interest.
Significance of Impact
Consequence
Probability
Moderate
Likely
The terrestrial flora within and close to the project area mainly comprises thick vegetation and
forestry cover. Fauna distribution in this area is of minimal significance.
Mitigation Measures
Rosinvest will engage government in natural resource management to reduce the
disturbance on biodiversity in the area;
Rosinvest will not clear any vegetation along the rivers and streams in the area; and
Vegetation will only be cleared in areas that will be directly affected by the project.
Impact Classification
The impact on biodiversity will be direct and irreversible.
Effectiveness of the proposed measures
The proposed measures are likely to be 98% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
Life of the Project.
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6.3.3.8
ROSINVEST -EIS
Cultural Heritage and Archaeological Sites
Cause and Comment
From a survey of the site and discussions with the people living near the project area, it was
revealed that no known affirmed archaeological or cultural sites exist within the areas to be
developed for mining activities.
6.3.3.9
Solid Waste
The major solid wastes to be generated at the Rosinvest Mine Project are mine wastes (waste
rock, overburden and tailings) and general solid waste. The mine waste will be stored on waste
rock and overburden dumps and tailings storage facilities. General waste will be handled in
different ways and will need a solid waste strategy for effective management.
Cause and Comment
Rosinvest endeavors to adhere to the Waste Management Regulations, 112 of 2013 Part 4 (SI
No. 18). which provides for the control of transportation of waste and management of waste
disposal sites.
Significance of Impact
Consequence
Probability
Major Impact
Very Likely
Waste Management Strategy
The waste management strategies proposed for the Project consider waste from the concept and
planning stages through design, construction, operation and decommissioning. The strategies aim
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to minimise environmental harm that could occur if wastes are not managed properly and
contaminants impact environmental values.
The strategy ensures compliance with regulatory requirements as a minimum and incorporates
the waste minimisation hierarchy in order of preferred options:
Waste Avoidance;
Waste Re-Use;
Waste Recycling;
Energy Recovery From Waste, And
Waste Disposal.
Waste generated on the Project site during the construction, operation and decommissioning
phases would be minimised through:
Assessment of Waste Reduction Opportunities For Identified Waste; And
Management of Waste In Accordance With the Waste Minimisation Hierarchy.
The strategy would also address monitoring, tracking and reporting of waste. ROSINVEST
would consult with the Kalomo District Council and ZEMA waste management strategies for the
Project.
Mitigation Measures
General waste
General wastes would be collected regularly and transported for disposal at the Kalomo District
Council and ZEMA licensed dump site.
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Some solid wastes, such as cardboard packaging and wooden pallets would be reused on-site for
other purposes where practical. Scrap steel, batteries, toner cartridges, and other recyclables
would be recycled off-site by third parties where feasible.
Regulated wastes would be stored in appropriate locations and conditions, until they can be
transported off-site by a licensed regulated waste contractor.
Effectiveness of the proposed measures
The proposed measures are likely to be 95% effective. These measures will be reviewed and
periodically updated to enhance their effectiveness to reflect knowledge gained during the course
of the project‟s construction.
Duration:
Life of the Project.
6.3.3.10
Customary Land Rights
Cause and Comment
The project site is located in HRH Chief Simwata Chela. The implementation of the project will
entail the conversion of the land to a mining licence area and the restriction of activities which
the local people have been conducting in the area.
If not properly managed, the project has a potential to bring conflicts between the Rosinvest and
the local population.
Significance of Impact
Consequence
Probability
Major Impact
Very Likely
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The project area has no cultivated fields. Implementing the project will not result in the loss of
fields, cultivated crops, human displacements or livelihood.
Impact Classification
The impact on customary rights will be direct.
Effectiveness of the proposed measures
The proposed measures are likely to be 100% effective.
Duration:
6.4
Life of the Project.
OPERATIONAL PHASE ENVIRONMENTAL IMPACTS AND MITIGATIONS
6.4.1
Introduction
This section assesses the potential environmental impacts during the Mining (Operational) phase
of the Project. The production and auxiliary facilities proposed for this project will be used for
the forty-year life of the Project.
This section describes these potential environmental impacts and recommends management and
mitigation measures during the operating phase.
The majority of the impacts assessed fall in the moderate category in terms of consequence and
are likely to occur, however mitigation measures are outlined to explain how these impacts can
be reduced to acceptable levels.
Operations will have a moderate impact on ambient dust levels in the Project area due to mining
machinery and vehicles. In addition there will be risks with regards to surface and groundwater
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conditions from potential seepage and silt runaways from waste rock dumps.
The majority of catastrophic impacts are related to unlikely to highly unlikely events such as
chemical spills and spills from storage facilities. Strict procedures will be in place for mining
operations (OMP) to ensure such events remain highly unlikely. There are no likely or very likely
catastrophic impacts from the Project operating phase.
An Environmental Management Plan (EMP) has been developed which incorporates the
findings of this EIS into a series of categories for implementation.
6.4.2 Environmental Impacts – Mining (Operational) Phase
6.4.2.1
AIR POLLUTION
Major environmental aspects that contribute to air pollution at the mine will include haulage of
waste from the pit to the dumpsites, haulage of the raw material from the pit to the processing
plant and road maintenance activities. The matrix table below presents the environmental risk of
air pollution without and with mitigation measures.
Table 9:- Air Pollution
Air Pollution Due to Dust Generation from Open Spaces, Pit, OB and Access Roads
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Local
Likelihood (L)
Definite
Proposed Mitigation Measures
1) Water shall be sprayed along the ramps, access roads and open spaces using a water
bowser.
2) Appropriate protective clothes such as dust masks, goggles and work suites shall be
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provided to workers operating earth moving machines and dumping supervisors.
3) New employees shall be inducted on safety requirements when working in dust prone
areas and safety talks shall be conducted frequently.
4) Signs shall be installed to educate workers about the health dangers of inhaling small
particles of dust.
5) Annual medical check-ups shall be conducted to determine the levels of dust exposure
to workers.
6) Ambient dust around the mine area shall be monitored monthly to ensure that the dust
fall-out around mining activities is below the ZEMA limit of 250 mg/m2/day.
Air pollution After Applying Mitigation Measures
Magnitude (M)
Negligible
Duration (D)
40 years
Extent (E)
Activity Specific
Frequency (F)
Daily
Likelihood
6.4.2.2
Definite
WATER AND SOIL POLLUTION
Key environmental aspects that will contribute to water and soil pollution are generation of
hydrocarbon waste due to servicing of mining machines and distribution of fuel. Other activities
are domestic waste water, sewage disposal, dewatering activities and surface water run-off. The
overall environmental risk before and after mitigation measures is predicted in the table below.
Table 10:- Water and Soil Pollution
Water and Soil Pollution Without Mitigation Measures
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Activity Specific
Likelihood (L)
Possible
Proposed mitigation measures
1) All the de-watering water shall be directed into a settling pond in order to settle solids
first before the water can overflow as discharge.
2) The effluent shall be monitored weekly for Conductivity, Dissolved Oxygen, pH and
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Total Dissolved Solids using a potable field water monitoring instrument. Samples
shall also be analyzed using a reputable laboratory at least once in three months.
3) A perimeter drain shall be constructed around the camp, pit and the OB to facilitate
trapping of all the solids that may be washed by storm water.
4) A standard workshop with a dedicated storage facility and generation facilities for
hazardous waste shall be constructed. This shall be concrete lined, signs shall be
installed and a water/oil separator shall be installed for all the effluent from the
workshop and the washing bay.
5) A wash-bay for heavy machines as well as light vehicles shall be constructed and this
shall be concrete lined with a perimeter drain connected to a silt trap for capturing
solids from washing activities. The overflow from the washing bay silt trap shall be
directed into the central oil/water separator for trapping possible hydrocarbons from
washing activities.
6) All the hazardous wastes shall be segregated and stored within the workshop in a
dedicated hazardous waste storage room. These wastes shall include used fluorescent
tubes, used oil filters, expired fire extinguishers, used batteries and hydrocarbon
contaminated waste.
7) Disposal of hazardous waste shall be done using a licensed waste collection company
for appropriate disposal.
8) Spills containment facilities such as absorbents, drip trays, wheelie bin, shovel and oil
booms shall be made available at all points where hydrocarbons shall be handled.
9) A bio-remediation farm shall be established within the mine area for treatment of
hydrocarbon contaminated soils by mixing it with nitrogen based fertilizer, effluent
from the modular sewage treatment plant and by frequent aeration.
10) Domestic water and sewage waste are disposed off through septic tanks.
11) All employees shall be subjected to environmental inductions in order for them to be
aware of water and soil pollution control measures.
Water and Soil Pollution After Applying Mitigation Measures
Magnitude (M)
Minor
Duration (D)
40 years
Extent (E)
Local
Frequency (F)
Monthly
Likelihood (L)
Highly Unlikely
6.4.2.3
NOISE AND VIBRATION
Environmental aspects that will contribute to noise and vibration are movement of earth moving
machines, drilling activities, operations of the generator and blasting activities. Some of these
activities are continuous while others are intermittent. For examples, the generator will run about
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12 hrs. per day while blasting will be done only once per day. The table below presents the
predicated environmental risk with mitigation measures and without mitigation measures.
Table 11:- Noise and Vibration
Noise and Vibration Without Mitigation Measures
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Activity Specific
Likelihood (L)
Definite
Proposed Mitigation Measures
1) Controlled blasting shall be introduced to minimize noise and vibration during
blasting.
2) All the machinery shall be serviced according to manufacturer manuals to ensure that
they operate according to standards.
3) Noise and vibration monitoring shall be conducted frequently according to the
monitoring plan to determine intervention measures.
4) Appropriate Personal Protective Equipment/Clothes shall be provided to all the
workers and this shall be used in high noise areas.
5) All activities with potential to generate significant noise and vibration shall be
conducted during the normal working hours of the day.
6) The blasting schedule shall be maintained and this schedule shall continue taking
about 30 minutes every day when blasting is done.
Noise and Vibration After Applying Mitigation Measures
Magnitude (M)
Marginal
Duration (D)
40 years
Extent (E)
Local
Frequency (F)
Monthly
Likelihood (L)
Highly Unlikely
6.4.2.4
LOSS OF FLORA AND FAUNA
Project activities that interact with flora and fauna are disposal of overburden material, extension
of the pit, road maintenance activities, maintenance of the surrounding and maintenance of the
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firebreak/security patrol road around the camp. The environmental risk for flora and fauna was
predicted as explain in the matrix table below.
Table 12:- Loss of Flora and Fauna
Loss of Flora and Fauna Without Mitigation Measures
Magnitude (M)
Marginal
Frequency (F)
Annual
Duration (D)
40 years
Extent (E)
Activity Specific
Likelihood (L)
Possible
Proposed mitigation measures
1) Site clearing shall be limited to development areas and before any clearing is done,
the Mine Manager shall issue a site clearing approval in consultation with the SHES
Manager.
2) Biological monitoring of trees and animal species around the mine area shall be
undertaken once per year.
3) No charcoal burning shall be tolerated within the mine licence area and the mine shall
not buy charcoal from the community as this may promote charcoal burning by the
community. All cooking activities shall be done using a stove and only dead-wood
shall be collected from the forest as firewood for general purposes.
4) Trapping of wild animals and buying of illegal game meat shall be included in the
disciplinary code for all employees and applicable disciplinary measures shall be
instituted to erring employees in accordance with Labor Laws.
5) A firebreak shall be prepared every year around the mine licence area before the fire
burning season starts to protect flora and fauna within the mine area.
6) Security patrols shall be conducted in the entire mine area to monitor deforestation
activities which shall be considered as trespass and necessary legal actions shall be
instituted to offenders.
7) Wildlife conservation awareness campaigns shall be conducted once per year for
workers and the community.
8) Protection measures for flora and fauna shall be part of the material for environmental
inductions.
Loss of Flora and Fauna After Applying Mitigation Measures
Magnitude (M)
negligible
Duration (D)
40 years
Extent (E)
Local
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Frequency (F)
Annually
Likelihood (L)
Highly Unlikely
6.4.2.5
NON-HAZARDOUS AND HAZARDOUS WASTE MANAGEMENT,
CHANGE OF LANDSCAPE AND LAND DEGRADATION
Key environmental aspects that contribute to change of landscape and land degradation will
include the open pit, disposal of overburden material at the OB dump, domestic waste from the
camp and clearing of access roads. Of significance however are the OB dump and the pit. The
table below presents the overall environmental risk before and after mitigation measures.
Table 13:- Non-Hazardous and Hazardous Waste Generation
Non-Hazardous and Hazardous Waste Generation and Disposal and Change of
Landscape and Land Degradation Without Mitigation Measures
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Activity Specific
Likelihood (L)
Definite
Proposed Mitigation Measures
1) Once production starts, all the material from the mine shall be used as backfilling
material for the pit as a measure to reduce the volume of waste to the OB dump.
2) Once backfilling starts, the OB dump shall be re-vegetated with local flora species
and this shall add to the aesthetic value of the area.
3) At closure, the OB dump shall fully be re-vegetated and the pit shall be stabilized to
let it steadily fill with water.
4) Re-vegetation activities shall be extended to the camp to close up spaces that will be
cleared.
5) All the domestic waste from the camp shall be collected in dedicated waste bins and a
land fill shall be constructed within the mine licence area for disposal. The landfill
shall be licensed by ZEMA and licence conditions for managing it shall be complied.
6) All the hazardous waste from the mine shall be collected by licensed transporters.
7) Hazardous waste that may not have commercial value shall be disposed off at a
licensed dumpsite that will be operated at the mine or kept within the storage house
awaiting appropriate disposal.
8) Sludge from sewage treatment plant will be dried on a drying pan and thereafter used
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as manure for the re-vegetation of the dump site. The sludge has undergone
decomposition and it is no hazardous.
Non-Hazardous and Hazardous Waste Generation and Disposal and Change of
Landscape and Land Degradation After Mitigation Measures
Magnitude (M)
Significant
Duration (D)
40 years
Extent (E)
Activity specific
Frequency (F)
Daily
Likelihood (L)
Possible
6.4.2.6
OCCUPATIONAL HEALTH AND SAFETY
Main environmental aspects associated with occupation health and safety will include blasting,
loading and offloading waste, transportation of waste and raw material and general maintenance
activities. Contributing factors to risk assessment are dust, noise, explosions, fire and failure to
follow machine operating procedures. The table below presents the risk assessment for
occupational health and safety.
Table 14:- Occupational Health and Safety
Occupational Health and Safety Without Mitigation Measures
Magnitude (M)
Catastrophic
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Project Site
Likelihood (L)
Definite
Proposed Mitigation Measures
1) Annual medical check-ups shall be done for all the workers and where health related
problems are advised for some workers by medical experts, jobs may be changed for
such workers or they may be retired on medical grounds.
2) Safe working procedures shall be developed following approval of this report for high
risk operations such as handling of explosives, haulage of material, working with
electrical facilities and servicing of machines. These procedures shall be reviewed
annually to keep them up to date with changes.
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3) Safety audits shall be conducted using an independent and qualified Auditor and
recommendations in the Audit report shall be enforced.
4) Safety and Environmental weekly discussions shall be conducted to remind all the
workers about safe practices.
5) Safe practice observers/spotters shall be appointed and these shall also be responsible
for activities such as supervising end-tipping of the overburden.
6) Safety statistics shall be reported weekly and the figures shall be displayed on a notice
board that shall be established within the camp.
7) All accidents and near-misses shall be reported to the Safety, Health and
Environmental Manager and failure to report shall result into disciplinary measures.
8) For the general safety of employees in the camp, the security manager shall continue
being in charge of patrols and inspections within the pit, Overburden Dump and the
camp.
Occupational Health and Safety After Applying Mitigation Measures
Magnitude (M)
Significant
Duration (D)
40 years
Extent (E)
Activity specific
Frequency (F)
Daily
Likelihood (L)
Possible
6.4.2.7
SOCIAL CHALLENGES FOR EMPLOYEES
Employees will be staying in a camp from Monday to Friday and they will be taking a weekend
off. In addition, they will be entitled to their annual leave days. This practice shall continue.
However, there are social challenges with this schedule mainly family related hence the need to
consider the working schedule as an aspect that has potential to cause social conflicts. The risk
assessment and mitigation measures are presented below.
Table 15:- Social Challenges by Employees
Social Challenges by Employees Without Mitigation Measures
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Province
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Likelihood (L)
ROSINVEST -EIS
Definite
Proposed Mitigation Measures
1) A social Counseling Expert shall be engaged once every year to provide counseling
services on various social issues to all workers and a separate session shall be
organized through the General Manager for all the miner‟s wives.
2) Employees and their wives shall be allowed to present employment caused social
challenges to the General Manager for assistance or referral to counseling experts.
This shall be handled with maximum recognition of the human right to privacy and
confidentiality, hence only professional and registered counselors shall be engaged to
provide the service.
3) The working schedule shall be maintained as this facilitates time for employees to be
with their families and annual leave shall be mandatory.
Social Challenges by Employees After Applying Mitigation Measures
Magnitude (M)
Marginal
Duration (D)
40 years
Extent (E)
Province
Frequency (F)
Daily
Likelihood (L)
Possible
6.4.2.8
CONFLICTS WITH THE LOCAL COMMUNITY AND NEARBY
MINES
For a project with environmental and social impacts, grievances are part of the development
process. It does not matter what level or amount of resources have been invested in corporate
social activities when it comes to grievances because it is not possible to please everyone in life.
Besides, it is human nature to view same issues differently and this difference in perception is
what makes social diversity and dynamics.
Rosinvest Zambia Limited recognizes the need to consider and address conflicts with the
community because this builds a good relationship, reduces the cost of resolving some conflicts,
it is a good alternative to litigation and the approach protects the corporate image.
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To avoid subjective decisions, it is imperative to have guiding rules for resolving social conflicts
and this is the approach adopted by the company. The table below presents the social risk
associated with the project before mitigation measures and after mitigation measures.
Table 16:- Conflicts With the Local Community and Nearby Mines
Conflicts With the Local Community and Nearby Mines Without Mitigation Measures
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Province
Likelihood (L)
Definite
Proposed Mitigation Measures
1) A grievance mechanism shall be developed by an independent and competent
consultant and shall be implemented within Six (6) months following approval of this
report. The mechanism shall be established to receive record and address stakeholder
concerns which shall be related to mining activities. The mechanism shall be
developed in a participatory manner.
2) The grievance mechanism shall be based on the extent of risk and adverse impacts
discussed in this report
3) Grievances shall be addressed promptly, in an understandable and transparent process,
which shall be culturally appropriate and readily accessible to all the Interested and
Affected Parties (IAPs) including vulnerable groups.
4) A system shall be put in place to ensure that grievance submission does not result into
costs and/or retribution.
5) Once the mechanism is endorsed by the General Manager, it shall be
publicized through consultative meetings and Community Representatives to facilitate
with receipt of grievances shall be appointed.
Conflicts With the Local Community and Nearby Mines After Applying Mitigation
Measures
Magnitude (M)
Minor
Duration (D)
40 years
Extent (E)
Province
Frequency (F)
Daily
Likelihood (L)
Possible
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6.4.2.9
ROSINVEST -EIS
HIV/AIDS RELATED CHALLENGES
It is commonly said that “if you are not infected by HIV/AIDS, then you are affected”. The
statement is absolutely true and the HIV/AIDS pandemic has since become part of the
development process. As such, government through the Ministry of Health has mainstreamed the
HIV/AIDS challenge in all sectors of the economy. Large scale mining is not exempted. The
table below predicts the HIV/AIDS challenge without mitigation and after intervention.
Table 17:- HIV/AIDS Related Challenges
HIV/AIDS Related Challenges Without Mitigation Measures
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Province
Likelihood (L)
Definite
Proposed Mitigation Measures
1) A professional HIV/AIDS Counselor shall be subcontracted once every year to offer
awareness, voluntary counseling and testing services to employees.
2) The company shall also extent the voluntary counseling and testing services to the
mining area with assistance from relevant institutions offering the service.
3) HIV/AIDS related medical information shall be strictly confidential and shall not
affect any form of recruitment.
4) Workers who may voluntarily come out with the aim of creating awareness and
stopping stigmatization shall be encouraged.
5) A company policy on HIV/AIDS shall be developed and implemented within Six (6)
months following approval of this report and distribution of condoms in toilets shall
be part of the policy.
6) Employees on Anti-Retro-Viral treatment shall be supported.
HIV/AIDS Related Challenges After Mitigation Measures
Magnitude (M)
Minor
Duration (D)
40 years
Extent (E)
Province
Frequency (F)
Daily
Likelihood (L)
Possible
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6.4.2.10
ROSINVEST -EIS
DISEASE VECTOR FROM PITS AFTER CLOSER
After closure, water will accumulate in the pits and form ponds. This may probably be the
sources for potential disease vectors such as mosquitoes. The ponds also pose danger to the
community who may want to swim and fish in these ponds.
Table 18:- Disease Vector
Disease Vector from Water that Have Accumulated in the Pits
Magnitude (M)
Significant
Frequency (F)
Daily
Duration (D)
40 years
Extent (E)
Province
Likelihood (L)
Definite
Proposed Mitigation Measures
1) The proposed project site will be fenced and security will be on guard even after
closure.
2) Spraying for mosquitoes will be done at regular intervals according to guidelines from
the Ministry of Health.
3) No one will be lowed to swim in the ponds formed in the pits.
4) No one will be allowed to do any fishing in the ponds.
5) Ponding during operation phase will be avoided by putting in place a dewatering and
water pumping program.
6) No settlements will be allowed around the pit periphery and inside the mine licence
areas.
7) No one will be allowed to use the pond water for domestic and portable water use.
8) Water tests will be carried out to ascertain its quality.
HIV/AIDS Related Challenges After Mitigation Measures
Magnitude (M)
Negligible
Duration (D)
40 years
Extent (E)
Activity Specific
Frequency (F)
Daily
Likelihood (L)
Possible
Other Environmental Impacts will include;
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6.4.2.11
ROSINVEST -EIS
Reduction in Ground Water Quantity
Nature and Source of Impact: Constant water abstraction from the mine to keep it in workable
condition has potential to reduce the ground water levels.
However, the aquifer at the project site is enormous and the amount of water that will be
abstracted during operations will not result in any significant reduction in ground water levels.
Impact Significance: Non significant
Proposed Mitigation Measures: Schedule dewatering operations targeting work areas only
allow the mine to flood at the end of mining operations.
6.4.2.12
Reduction in Ground Water Quality
Nature and Source of Impact: Indiscriminate disposal of solid and liquid wastes has potential
to contaminate ground water through seepage. These may include oil and fuel from operation
and servicing of equipment, material spillage, improper disposal of waste, etc.
Impact Significance: Moderate
Proposed Mitigation Measures: Prevent material spillage, contain all wastes and spilled
material, dispose of wastes in designated disposal sites, clean up and remediate all contaminated
sites.
6.4.2.13
Disturbance to Geological Integrity
Nature and Source of Impact: Mining activities involving blasting and excavation by nature
has potential to affect geological integrity by weakening the strata due to vibrations mainly from
blasting operations. However, being an open pit mine the effects are relatively minimal as they
do not affect much of the underlying strata.
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Impact Significance: Low
Proposed Mitigation Measures: Observe standard blasting guidelines for opencast mining and
use only explosives with approved power rating.
6.4.2.14
Loss of Soil Fertility
Nature and Source of Impact: Removal of ground cover and top soil on clearing land for Tin
mining leads to loss of soil fertility making it difficult for plant growth without remediation.
Impact Significance: Moderate
Proposed Mitigation Measures: Stockpile top soil for re-profiling back progressively after
mining each respective area.
6.4.2.15
Reduced Soil Stability
Nature and Source of Impact: Removal of ground cover and top soil on clearing land for
limestone and shale mining leads to loss of soil stability making it readily prone to agents of
erosion.
Impact Significance: Low
Proposed Mitigation Measures: Minimise area disturbed and ensure all worked areas are
adequately compacted and re-vegetated after use.
6.4.2.16
Loss of Biodiversity and Disturbance to Natural Lands and
Geographical Resources
Nature and Source of Impact: Loss of land cover and habitat destruction arising from Tin
mining results in loss of biodiversity as plant life and animals are lost in the process and their life
support systems are disrupted.
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Similarly, discharge of high levels of sediments into the aquatic environment also disturbs
aquatic life and its productivity thereby limiting biodiversity. However, overall effects on
biological diversity, natural lands and geographical resources are negligible. This is due to the
relatively small area of project footing and relatively nontoxic emissions. Further, increased
supply of water to the nearby wetland is an enhancement factor compensating for the lost
biodiversity. The absence of endangered species in the project area and the relatively rich
diversity of plant life in the area surrounding the project site is another compensating factor.
Impact Significance: Low
Proposed Mitigation Measures: Limit disturbance of habitat by keeping the plant and mine
footing to minimal requirements together with adequate treatment of waste streams and
progressive rehabilitation of disturbed areas. Further action will involve planting of flowers,
lawn and fruit trees together with some indigenous trees found in the area in a well landscaped
manner.
6.4.2.17
Disturbance to Aquatic Life
Nature and Source of Impact: Discharge of process water and sediment loaded storm water
into the aquatic environment has potential to disturb aquatic life.
Impact Significance: Low
Proposed Mitigation Measures: Ensure all discharges from the plant and mine sites pass
through sediment traps and comply with licensed discharge limits. Regularly maintain sediment
traps for efficient operation.
6.4.2.18
Ecological Disturbance and Effect on Climatic Conditions
Nature and Source of Impact: Establishment and operation of the mine will disturb the
ecological setting of the area thereby rendering it less conducive a habitat for both plant and
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animal life through physical disturbance and discharge of pollutants. On the other hand the
presence of a large water-body creates a habitat with favourable conditions for breeding of
mosquitoes especially at the end of the project life when disturbing activities will have ceased.
Such insects being disease vectors for malaria have potential to negatively affect human health.
Minor changes are likely to have occurred in micro weather conditions within the confines of the
factory. The main elements likely to be affected are humidity and temperature while rainfall,
wind and sunshine are unlikely to be affected. Although the changes have not been monitored to
that effect it is unlikely that the same would be significant enough to affect the climatic
conditions of the area. Consequently project impacts on the climatic conditions of the area are
considered to be insignificant.
Impact Significance: Low/Moderate
Proposed Mitigation Measures: Limit disturbance of habitat by keeping the mine footing to
minimal requirements together with adequate treatment of waste streams and progressive
rehabilitation of disturbed areas to enhance life support systems.
6.5
SOCIAL IMPACT ASSESSMENT
6.5.1
Introduction
The identification of the potential social impacts that may result from project development is
based on a review of the project design and industry experience. These impacts include
aesthetics, noise, air quality (dust and pollutants), vibration, water discharge and runoff,
subsidence, waste sources include the open pit and surface infrastructure and access or haul
roads. If mining will cause quality deterioration of either surface water or groundwater,
remedial and treatment measures must be developed to meet discharge standards.
The potential impacts were also identified through site visits during the collection of baseline
data and during interactions with the local communities. Five factors were considered when
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assessing the significance of all the social impacts, namely:-
1. Relationship of the impact to temporary (relating to measured time) scales - the temporal
scale defines the significance of the impact at various time scales, as an indication of the
duration of the impact.
2. Relationship of the impact to spatial (relating to space) scales - the spatial scale defines
the physical extent of the impact.
3. The severity of the impact - the severity/beneficial (state or extent of badness or benefit)
scale is used in order to scientifically evaluate how severe negative impacts would be, or
how beneficial positive impacts would be on a particular affected system (for ecological
impacts) or a particular affected party. The severity of impacts can be evaluated with and
without mitigation in order to demonstrate how serious the impact is when nothing is
done about it. The word „mitigation‟ means not just „compensation‟, but also the ideas of
containment and remedy. For beneficial impacts, optimization means anything that can
enhance the benefits. However, mitigation or optimization must be practical, technically
feasible and economically viable.
4. The likelihood (degree of probability) of the impact occurring the likelihood of impacts
taking place as a result of project actions differs between potential impacts. There is
often no doubt that some impacts will occur (e.g. loss of vegetation), but other impacts
are not as likely to occur (e.g. vehicle accident), and may or may not result from the
proposed development. Although some impacts may have a severe effect, the likelihood
of them occurring may affect their overall significance.
5. Each criterion is ranked with scores assigned as presented in Table 6-10 (shown below)
to determine the overall significance of an activity. The criterion is then considered in
two categories, viz. effect of the activity and the likelihood of the impact. The total
scores recorded for the effect and likelihood are then read off the matrix presented in
Table 6-11, to determine the overall significance of the impact. The overall significance
is either negative or positive.
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6.5.2
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Impacts and Mitigations Measures
6.5.2 .1
Impact on Local Communities and Complaints
Cause and Comment
There is a possibility of complaints from the people from the communities especially those in
headman James which are closer to the proposed mine site. The following issues are likely to be
the sources of concern: Disturbance of footpaths – People will likely complain that the project will disturb the
footpaths that they use in the area;
Loss of farming plots on the footprint of the area of interest for the mine;
Fear of drawing water from the local streams perceived to be contaminated by mine
operations; and
Noise and Dust from the mine trucks operating in the area.
Significance of Impact Low to Moderate
Mitigation Measures
Farming within the area of interest will be discouraged.
Dust on the haul road will be regularly be suppressed by spraying water;
People drawing water from local Chilobe and Chana streams will be regularly informed
on the quality of the water in these water facilities;
Only equipment with noise levels up to 82dBA (measured at source) will be allowed to
operate at the mine and people will be sensitized on concentrating their daily activities
about 24m from the edge of the road;
Signposts will be erected on all graveyards in the area. ROSINVEST will liaise with the
council on the choice of the cemetery which should remain active in the area ;
ROSINVEST will implement speed retardants and limits on the mine roads to 50km/h
for safety reasons;
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ROSINVEST will ensure that roads are kept clear of any debris and are smooth to avoid
noise and vibration; and
ROSINVEST will engage the communities living along the haul road throughout the
project life.
Impact Classification
The negative impacts on the community will be cumulative and reversible.
6.5.2 .2
Impact on the Establishment of Sound Relationships
Cause and Comment
Leaders of the people in the area (Traditional Leadership and government leaders) will be
involved from the inception to avoid the misunderstanding between the proponent and the
local community.
Significance of Impact Low to High
Mitigation Measures
Consultations relating to mine developments and other activities will constantly be relayed to
community leaders through ROSINVEST public relations office.
Impact Classification
The impact of establishing sound relationship with the community will be a cumulative and
reversible.
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6.5.2 .3
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Impact on Economy – Local, Regional and National
Cause and Comment
The project will enable ROSINVEST establish a mine in an area which could improve
economically once the mine starts operating. This will create jobs in the local area, district and
regional level.
Decommissioning and closure unfortunately will be accompanied by possible job losses at the
mine. The local economy will likely be affected due to its high dependence on the mining and
related activities. If not mitigated or planned for, the impact will be severe for the
regional/national economy and the people involved.
Significance of Impact Low to High
Mitigation Measures
ROSINVEST will continue with its exploration program in order to establish new ore
sources; and
ROSINVEST will continue supporting diversification from mining activities in Chirobi
such as crafts, bee-keeping for honey and conservation farming;
Impact Classification
The impact on the regional and local economy will be a cumulative and irreversible.
6.5.2 .4
Impact on Procurement and supply of Goods and Services
Cause and Comment
Procurement of goods and services is expected to continue during construction and operations
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stage. Local procurement of materials and equipment is likely to be confined to relatively
specialized products which will be needed for the development and running of the mine.
ROSINVEST will procure goods and materials locally to the extent possible to ensure that
economic benefits are felt by the local suppliers and their employees.
ROSINVEST will ensure that procurement of good and services takes account of the manner
in which the material is produced, stored, transported so that good and services that violet
human rights and cause environmental degradation are avoided. Thus ROSINVEST will adopt
„cradle to grave‟ concept of monitoring.
Goods and service procurement is likely to be active at regional rather than local level,
therefore the spatial scope is defined as „regional.‟ However, even at the regional level, the
loss of business could have significant negative results.
Decommissioning and closure will be accompanied by fewer contracts for the supply of goods
and services. The local economy will likely suffer a significantly set back due to the loss of
such contracts. If not mitigated or planned for, the impact will be severe for the economy and
the companies/people involved.
Significance of Impact Low to High
Mitigation Measures
It is recommended that diversification of the economy be encouraged as early as possible by
both the mining companies and the government.
Impact Classification
The impact on procurement and supply of goods and services will be a cumulative and
reversible.
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6.5.2 .5
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Loss of Employment
Cause and Comment
There is a possibility that people (both from ROSINVEST and Contractors) will likely lose
employment, for various reasons, during construction and operations stages of the project. It is
expected though that major employment loss will be at Mine closure stage. Loss of
employment will negatively impact the affected families, the community (as a result of the
economic trickle-down effect) and the government (loss of taxes).
Significance of Impact Moderate to Low
Mitigation Measures
Counseling and skills development as part of closure planning may assist some contractors to
sustain their businesses post-closure. Community development initiatives are not to be
exclusive for social development, but can encourage business development and the
identification of business opportunities in the general mining environment.
Impact Classification
The impact of loss of employment will be direct and irreversible.
6.5.2 .6
Increased Business Activities
Cause and Comment
The development of the Rosinvest Mine Project will provide a lot of in Chirobi area. This will
help sustain, and possibly increase the current levels of business within the area and compel
government to improve infrastructure in the area.
Significance of Impact High to Moderate
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Mitigation Measures
Dissemination of information about the mine and its operation through the corporate
communications function (annual reports) will potentially inform local business sentiment.
The same mode of communication will be used to alert the local business community to
imminent decommissioning and to other mining developments.
Impact Classification
The impact of increased business activities will be cumulative and irreversible.
6.5.2 .7
Increased local risk of HIV/AIDS infection
Cause and Comment
The project is likely to attract a large number of job seekers from outside the community. This
population influx has the potential to increase the chances of the spread of HIV/AIDS
infections in the area. HIV/AIDS is not just a public health problem; it is a major development
crisis and will have implications on the operations of Rosinvest Mine Project. .
Significance of Impact Moderate
Mitigation Measures
ROSINVEST will implement an HIV/AIDS policy based on education and prevention, which
will be communicated to all employees. In practice, community, church and education groups
will be encouraged to support this initiative
Impact Classification
The impact of increased local risk of HIV/AIDS infection will be cumulative and irreversible.
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6.5.2 .8
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Employees Health and Safety
Cause and Comment
ROSINVEST considers the safety and health of employees and contractors as paramount and
a fundamental requirement for continued operation and growth.
Pre-employment and periodic medical examinations will be conducted on all mine employees.
As a minimum, the baseline medical examination would include the following:
A short medical history of the employee and his family history;
Full occupational history of the employee;
Signature of the employee to state that the above information is accurate and correct;
Examination of:
Weight
Height
Blood pressure
Pulse
Urine test
Eye Test (Snelling Chart)
Chest X-ray (large 35 cm x 43 cm)
Audiometry test - physical and visual inspection of both ears
Lung function
Cardio-respiratory examination (general physical examination)
A Doctor and trained staff will perform the employee medical examinations.
ROSINVEST will provide well-equipped sanitary facilities for its employees. Workers will
be encouraged to wash or shower frequently, particularly those employees exposed to dust,
chemicals or pathogens.
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Workers in areas of high temperature and/or humidity will be allowed to take frequent breaks
away from these areas.
The Company‟s Chief Medical Officer will keep a record of employee medical examinations,
specific surveillance records and medical history.
Significance of Impact High to Low
Mitigation Measures
Personal Protective Equipment (PPE) refers to protective clothing, helmets, goggles, or other
garments designed to protect the wearer's body or clothing from injury by blunt impacts,
electrical hazards, heat, chemicals, and infection, for job- related occupational safety and
health purposes. The following mandatory PPE would be required in all external areas within
the Project area:
Safety Helmet;
Steel-Cap Boots;
Safety Glasses; and
High-Visibility Clothing.
6.5.2 .8.1
Dust and Gas
ROSINVEST would implement particulate and gas/vapour exposure controls which would
apply to dust, fibres, mist, fume (including diesel particulates), gas, and vapour exposure in
the workplace. The controls would cover, amongst other things, evaluation of particulate and
gas/vapour hazards, and development of a control program to ensure that employees and
contractors do not suffer adverse health effects in the work environment from particulates or
gas/vapours, either used or generated by the mine.
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6.5.2 .8.2
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Noise
The following controls would be implemented throughout construction and operation to ensure
employees and contractors would not suffer adverse health effects from noise generated in the
workplace:
all noise sources in their area would be identified and assessed at least quarterly;
noise sources in their area would be reassessed after any significant change;
areas where hearing protection is required would be mapped and appropriately
signposted;
where hearing protection is required a range of hearing protection devices that are
approved for site would be available;
training would be provided in fitting, maintenance and the limitations of hearing
protectors;
there would be documented procedures for inspection, assessment, and maintenance of
noise reduction devices and noisy equipment to ensure noise levels are minimised;
employees would be given information, instruction and training regarding noisy
environments, including the hazards, potential health effects and control mechanisms;
a formal review of the practicality of engineering controls would be conducted annually
in areas where a hearing conservation programme is required;
each area where hearing protection is routinely worn (i.e. employees are exposed to
noise levels greater than 82dB(A) would have a plan of action for the control of noise;
and
All employees would attend audiometric testing as required.
With the implementation of these control measures, the residual health risks associated with
noise and vibration are expected to remain moderate.
6.5.2 .8.3
Raw Water
Water pumped from the open pits will be used as raw water for the operations at the mine.
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Boreholes will be sunk to supply drinking water.
The risk of unsafe drinking water is considered to remain low.
6.5.2 .8.4
Waste
All first-aid facilities would be equipped with gloves and other protective equipment in
accordance with standard medical practice. Clinical waste would be segregated and incinerated.
Personnel are also at risk of bacterial or infectious disease when cleaning change houses and
toilets. Safe operating procedures would be developed for this work, including the use of
appropriate PPE and hygiene practices (e.g. washing hands before consuming food).
With the proposed control measures in place, the risks associated with other biological hazards
are considered to be moderate.
6.5.2 .8.5
Hazardous Substances
Fuels (predominantly diesel), detergents, lubricants and oils, solvents, chemical for the leaching
and other processing chemical, degreasers, paints, resins and domestic cleaning agents would
form the majority of chemicals used at the mine site. The following controls would be
implemented:
All chemical will be accompanied with Material Safety Data Sheet (MSDS);
A register of all approved chemicals would be maintained;
All chemicals would be labelled and stored according to the requirements of the
respective MSDS and relevant Zambian Regulations. Copies of MSDS's would be kept
near storage areas;
PPE (e.g. gloves, face shields or respiratory-protection devices) and first-aid equipment
(e.g. emergency showers and eye-wash stations), as identified in the MSDS and/or risk
assessment would be maintained and available for use; and
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Training would be provided to employees and contractors through the site induction and
specific chemical awareness programs for relevant workers.
With the implementation of proposed controls, the residual health risk presented by hazardous
substances is expected to be moderate.
6.5.2 .8.6
Manual Tasks
Manual tasks requiring force, repetition or awkward postures can lead to musculoskeletal
injuries. As much as possible these types of tasks would be eliminated through good design.
Where required, lifting devices would be provided to reduce manual handling.
Manual Handling System will be implemented by the Project and will provide the following
controls:
good design, layout and practice, to minimise adverse health consequences due to
manual handling and vibration factors;
completion of an assessment of manual handling and vibration risks associated with a
task or activity; and
An assessment of ergonomic, manual handling and vibration risks for new plant or
equipment or modifications to existing plant or equipment.
With these controls in place, the risk of injury caused by manual handling injuries is low to
moderate.
6.5.2 .8.7
Poor Lighting
Poor lighting levels or the lack of emergency lighting in times of power failure or emergency
situations has the potential to cause hazard. The following would be provided for both
construction and operation phases to provide a safe and comfortable visual environment:
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task lighting;
access lighting, and
Emergency lighting.
ROSINVEST -EIS
The Project would implement Lighting System which requires lighting surveys to be carried out
in all areas with permanent lighting on a regular basis or following a major change.
With the implementation of proposed controls, the residual risk presented by poor lighting is
expected to be low.
6.5.2 .8.8
Injury from Vehicles
Vehicles on the proposed mine would include haul trucks, front-end loaders and light vehicles.
Collisions between these vehicles have the potential to cause serious injury to mine personnel
and members of the community. The following will be implementing to avert the impact:
Roads would be designed to comply with requirements of the Road Safety Standards in
Zambian and roads graded to an adequate safe level for the vehicles;
Construction workers and mine personnel operating vehicles on-site would be trained
and licensed, so that vehicles are driven in a safe and responsible manner;
Safe work procedures regarding driver safety (including speed limits) and dust control
would be implemented;
Speed limits around the site would be indicated by appropriate signage, and watering of
roads and access areas would be undertaken to suppress dust and improve visibility for
the driver;
Adequate lighting would be installed on-site to ensure night driving and operating
conditions are safe; and
Vehicle inspection checks would be undertaken as part of the routine maintenance
programme to control the risk.
The potential for injury from vehicles on the Project site during construction and operations is
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considered moderate.
6.5.2 .8.9
Injury from Machinery
Personnel may be at risk of interacting with moving machinery and vehicles resulting in
potentially serious injury. Hazards in this category may occur during the construction of
infrastructure, movement of heavy equipment, maintenance programs or repair work.
ROSINVEST‟s safe work procedure regarding the control of energized equipment and
machinery would be implemented incorporating isolation safety systems to reduce the likelihood
of exposure to sudden releases of all forms of energy to low levels. Appropriate speed limits and
traffic rules would be identified for the Project area. Barricades and visual demarcation would be
used to reduce the risk of pedestrian and vehicle interactions, as well as physical interaction with
other machinery.
The proposed controls would reduce the likelihood of occurrence personnel interacting with
moving machinery and therefore the risk to low levels.
6.5.2 .8.10
Fall from Height
There would be times where workers are required to work at height during the construction
phase (e.g. mine site building and the operation phase (e.g. maintenance of facilities).
ROSINVEST would plan activities so that work is performed at ground level where practical to
eliminate the requirement to work at heights. However, where working at heights
6
is
unavoidable, ROSINVEST would implement the following controls:
The hierarchy of controls are identified as follows:
1. Wherever possible work shall be performed from ground level.
2. In the event of raised plant and equipment, work shall be performed wherever
possible from permanently-positioned safe access to the task and work area.
3. Where this is not possible access via a temporary platform or elevated work platform
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can be used.
4. An alternative option is to use a person-fall restraint system that does not allow the
user to fall.
5. Only in the event that none of the above options are possible, the work can be
performed by using a fall-arrest system after obtaining a working-at-heights permit.
Personnel working at heights must be trained and deemed competent.
Tasks undertaken from elevated work platforms will be accompanied with fall protection
equipment to be worn at all times and connected to an approved anchor point.
With these controls in place, the risk of injury caused by a fall from height is low to moderate.
6.5.2 .8.11
Failure of Lifting Equipment
Items falling from height can also present a safety risk. PPE that protects against objects falling
from height include steel-capped boots and hard hats; will be worn in designated areas.
Failure of lifting equipment can result in serious injury. ROSINVEST will institute the following
controls:
only competent operators can set up, inspect or operate lifting equipment;
all lifting equipment would be inspected, maintained and stored to ensure the equipment
is able to function to its design specifications;
lifting equipment must be used within their Safe Working Load for the conditions of use;
and
A register of lifting equipment shall be maintained to record periodic inspections.
With these controls in place, the risk of injury caused by failure of lifting equipment is low to
moderate.
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6.5.2 .8.12
ROSINVEST -EIS
Shock from Electrical Installations
ROSINVEST will ensure that workers at electrical installation are protected by implementing
the following controls:
electrical equipment and installations shall be designed, installed and maintained to
ensure that:
1. persons are not able to contact exposed conductors energised at lethal voltages;
2. under fault conditions persons are not exposed to lethal voltages, currents or arc
flash;
3. under fault conditions equipment does not pose a fire risk;
4. control systems, including protection systems, emergency stopping systems and
safety alarms operate safely under all operating conditions, including power
supply instability or failure;
5. there is an effective means for positive isolation of equipment or an installation;
and
6. Prior to accessing any electrical equipment, the hazards should be well
understood and appropriate isolations, permits and PPE identified and
implemented.
electrical workers are competent for the tasks they perform;
electrical equipment is regularly tested and maintained;
earthling systems are installed and maintained, and
Electrical plans are developed and maintained for services on-site.
With these controls in place, the risk of injury caused by electrical energy is low to moderate.
6.5.2 .8.13
Risk of Injury in Confined Spaces
A confined space is an enclosed or partially enclosed space which is at atmospheric pressure
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during occupancy and is not intended or designed primarily as a place of work, and:
1. is liable at any time to:
have an atmosphere which contains potentially harmful levels of contaminant;
have an oxygen deficiency or excess; or
cause engulfment; and
2. Could have restricted means of entry and exit.
For such working environments, ROSINVEST will implement the following controls and
processes required to be in place prior to entry into a confined space, including:
assess and identify all confined spaces, including gas atmosphere testing;
ensure only trained and authorised persons are permitted to enter confined spaces
through use of a permit system;
ensure correct PPE is available for personnel working in confined spaces, and
Rapid recovery procedures.
With these controls in place, the risk of injury in confined spaces is low to moderate.
6.5.2 .8.14
Slips and Falls
Slips and falls is mainly associated with poor housekeeping, such as excessive waste debris,
loose construction materials, liquid spills, and uncontrolled use of electrical cords and ropes on
the ground, are also among the most frequent cause of lost time accidents at construction and
decommissioning sites. ROSINVEST will implement the following countermeasures:
Uphold good house-keeping practices, such as the sorting and placing loose construction
materials or demolition debris in established areas away from foot paths.
lifting equipment must be used within their Safe Working Load for the conditions of use;
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and
A register of lifting equipment shall be maintained to record periodic inspections.
With these controls in place, the risk of injury caused by failure of lifting equipment is low to
moderate.
6.5.2 .8.15
Shock from Electrical Installations
ROSINVEST will ensure that workers at electrical installation are protected by implementing
the following controls:
electrical equipment and installations shall be designed, installed and maintained to
ensure that:
1. persons are not able to contact exposed conductors energised at lethal voltages;
2. under fault conditions persons are not exposed to lethal voltages, currents or arc
flash;
3. under fault conditions equipment does not pose a fire risk;
4. control systems, including protection systems, emergency stopping systems and
safety alarms operate safely under all operating conditions, including power
supply instability or failure;
5. there is an effective means for positive isolation of equipment or an installation;
and
6. Prior to accessing any electrical equipment, the hazards should be well
understood and appropriate isolations, permits and PPE identified and
implemented.
electrical workers are competent for the tasks they perform;
electrical equipment is regularly tested and maintained;
earthling systems are installed and maintained, and
Electrical plans are developed and maintained for services on-site.
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With these controls in place, the risk of injury caused by electrical energy is low to moderate.
6.5.2 .8.16
Risk of Injury in Confined Spaces
A confined space is an enclosed or partially enclosed space which is at atmospheric pressure
during occupancy and is not intended or designed primarily as a place of work, and:
3. is liable at any time to:
have an atmosphere which contains potentially harmful levels of contaminant;
have an oxygen deficiency or excess; or
cause engulfment; and
4. Could have restricted means of entry and exit.
For such working environments, ROSINVEST will implement the following controls and
processes required to be in place prior to entry into a confined space, including:
assess and identify all confined spaces, including gas atmosphere testing;
ensure only trained and authorised persons are permitted to enter confined spaces
through use of a permit system;
ensure correct PPE is available for personnel working in confined spaces, and
Rapid recovery procedures.
With these controls in place, the risk of injury in confined spaces is low to moderate.
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6.6
ROSINVEST -EIS
IMPACT EVALUATION CRITERIA
The objective of this section is to predict and to assess these potential impacts and to recommend
mitigating measures to be incorporated into the project design.
The assessment of the issues has been conducted according to a synthesis of criteria required by
the integrated environmental management procedure defined below.
6.6.1
NATURE OF IMPACT
This is an appraisal of the type of effect the proposed activity would have on the affected
environmental component. Its description should include what is being affected and in what way.
6.6.2
DIRECT IMPACT
An impact that appears immediately as a result of an activity of the project, for example, the loss
of ecological habitat is a direct impact.
The direct impacts would be experienced mainly during the site preparation and clearing, and
include effects on the physical environment, health and safety of the workers during the
developmental phase.
6.6.3
INDIRECT IMPACT
An impact that is related to the project but it‟s of secondary nature. It only shows in an indirect
way. For example, the project may cause indirect impacts on the local economy of a community
by increasing accessibility to other markets or increased illegal settlements.
The indirect impacts are primarily socio-economic and extend beyond the project
implementation. The indirect impacts include changes in economic activities and long-term
changes, such as increased land degradation due to increased settlement and development at and
around the project site.
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Unlike the direct impacts, which occur in the immediate environment, the indirect impacts would
be felt in the adjacent regions.
6.6.4
SPATIAL EXTENT
The physical and spatial size of the impact is a description of whether the impact would occur on
a scale described as follows:Site, the impact could affect the whole or measurable portion of the site. Whether it is limited to
the immediate area of the proposed project;
Local, the impact could affect the extended area adjacent to the site perhaps a neighbourhood or
small town. Whether it would affect environs up to 15km outside the immediate environment;
Regional, that impact could affect the area including the outlying areas of the city, the transport
routes and the adjoining towns and National.
The impact could be as far as reaching
international boundaries.
6.6.5
FREQUENCY
Frequency is the incidence, occurrence, regularity, rate or rate of recurrence of the source of
impact. This is measured by the number of times of occurrence of the source of impact due to the
proposed development.
Occurs once, where the source of impact will either occur once or disappear with mitigation or
will be mitigated through natural process after occurring once due to the proposed development;
Occurs twice, where the source of impact will occur twice at any given phase of project
implementation and thereafter it will be entirely negated; and Occurs more than twice, where the
source of impact will continue or occur more than two times for the entire operational life of the
development, but will be mitigated by direct human action or by natural processes thereafter.
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6.6.6
ROSINVEST -EIS
DURATION
The lifetime of the impact; this is measured in the context of the life-time of the proposed
development.
Short term, the impact will either disappear with mitigation or will be mitigated through natural
process in a span shorter than the preparatory phase,
Medium term, the impact will last for the period of the preparatory phase, thereafter it will be
entirely negated,
Long term: the impact will continue or last for the entire operational life of the development, but
will be mitigated by direct human action or by natural processes thereafter,
Permanent: the only class of impact which will be non-transitory. Mitigation either by man or
natural process will not occur in such a way or in such a time span that the impact can be
considered transient.
6.6.7
INTENSITY
A description of whether or not the intensity (magnitude) of the impact would be high, medium,
low or negligible (no impact). An attempt will be made to quantify the impacts on components of
the affected environment to be described as follows: Is the impact destructive, or benign? Does it
destroy the impacted environment, alter its functioning, or slightly alter it? These are rated as
follows:-
Low, where the impact will not have significant influence on the environment, and this will not
be required to be significantly accommodated in the project design or implementation; the
impact alters the affected environment in such a way that natural processes of functions are not
affected in any significant way,
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
Moderate, where it could have an adverse influence on the environment, which would require
modification of the project design or alternative implementation schedules; the affected
environment is altered, however, function and process continue, albeit in a modified way,
High, where it could have significant influence on the environment but cannot be mitigated or be
accommodated by the project environment by introducing alternative mitigation measures, such
as realignment at a particular stretch or adoption of different design measures. Function or
process of the environment is disturbed to the extent where it temporarily or permanently ceases.
This will be a relative evaluation within the context of all the activities and the other impacts
within the framework of the project. Note that some impacts have a high intensity and a short
duration with no permanent audio effects.
6.6.8
SEVERITY
This describes whether the severity (harshness / gravity) of the impact would be high, medium,
low or negligible (no impact). The severity of the impact will be qualitatively determined on the
components of the environment to be affected by taking into consideration the following
questions. Is the impact harsh, serious or dangerous? Does it degrade the impacted environment,
alter its functioning, or slightly modify its natural state? These are rated as follows:-
Low applies where the impact is very little and will not have significant influence on the
environment. This will not be required to be significantly accommodated in the project design or
implementation and the impact changes the affected environment in such a way that natural
processes of functions are not affected in any significant way;
Moderate, applies where the impact could have an adverse influence on the environment and
would require some modification of the project design or alternative implementation schedules.
In this regard, the affected environment is altered while the function and process continue, albeit
in a modified way; and
High, applies where the impact could have significant influence on the environment but cannot
be mitigated or be accommodated by the project environment by introducing alternative
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
mitigation measures such as realignment at a particular stretch or adoption of different design
measures. In this regard, the function or process of the environment is disturbed to the extent
where it temporarily or permanently ceases.
6.6.9
PROBABILITY
This describes the likelihood of the impacts actually occurring. The impact may occur for any
length of time during the life cycle of the activity, and not at any given time. The classes are
rated as follows:-
Unlikely, the probability of the impact occurring is very low, due to the circumstances, design or
experience,
Possible, the impact could possibly happen, and mitigation planning should be undertaken,
Probable, it is most likely that the impact will occur at some or other stage of the development.
Plans must be drawn up before the undertaking of the activity,
Definite, the impact will take place regardless of any prevention plans, and only migratory
actions or contingency plans can be relied on to contain the effect.
6.6.10 SENSITIVITY
The sensitivity of the element being impacted would be regarded as being high, medium, low or
negligible (no impact). An effort will be made to determine the qualitative sensitivity of the
element of the environmental components being impacted upon due to the proposed
development. Is the reaction of the environmental component due to the impact acceptable or
not? Does it destroy the impacted environmental component, alter its functioning, or slightly
alter it?
Low, where the sensitivity of the element being impacted will not have significant influence on
the environmental component, and this will not be required to be significantly accommodated in
the project design or implementation. The impact to the affected environment will be in such a
way that natural processes of functions are not affected in any significant way;
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
Moderate, where the sensitivity of the element being impacted could have an adverse influence
on the environmental component, which would require modification of the project design or
alternative implementation schedules. The affected environment is altered while the function and
process continue and the albeit in a modified way; and
High, where the sensitivity of the element being impacted could have significant influence on the
environmental component but cannot be mitigated or be accommodated by the project
environment by introducing alternative mitigation measures, such as realignment at a particular
stretch or adoption of different design measures. The function or process of the environment is
disturbed to the extent where it temporarily or permanently ceases.
6.6.11 DETERMINATION OF SIGNIFICANCE
The community provides information on the characteristics of the impacts and the significance is
determined based on this information.
Significance is an indication of the importance of the impact in terms of physical extent, intensity
and time scale, and therefore indicates the level of mitigation required.
The classes are rated as follows:-
Negligible, the impact is not substantial and does not require any mitigatory action,
Low, the impact is of little importance, but may require limited mitigation,
Moderate, the impact is of importance and therefore considered to have mitigation. Mitigation is
required to reduce the negative impacts to acceptable levels or positive impacts maximised,
High, the impact is of great importance. Failure to mitigate, with the objective of reducing the
impact to acceptable levels, could render the entire development option or entire project proposal
unacceptable. Mitigation is therefore essential. Positive impacts should be enhanced as a priority.
From the baseline information assembled in the previous chapter coupled with the information
gained during the consultation stage, the expected environmental impacts can be categorised into
positive and negative impacts.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
In addition, it is important to consider the duration of the impact and at what phase of the project
it occurs, i.e. impacts during site preparation phase or impacts over the life of the (operational
phase) and whether the impacts are direct (i.e. removal of vegetation) or indirect (increased
sexual diseases as a result of the improved wages).
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
Table 19 Evaluation of Impacts
Phase
Description of Impact
Type of Spatial
Impact Extent
Improved Aesthetics of the Area
Enhanced aesthetics of Indirect/
Site
Preparation the project area by Direct
improving
the
and
and
Operational landscaping
general cleanness of
the mine.
Boosting Supplying Sector
positive boost to the
Site
Preparation local and national
economy through its
and
multiplier effect
Operation
Employment and Enhance Services
Employ
about
82
Site
Preparation people during all the
phases of theof the
and
Operational project.
Frequency
Duration
Intensity
Severity
Probability
Sensitivity
Determination
of Significance
Site
More than Long
twice
term
Moderate
Moderate
Probable
Moderate
High
Indirect/
Direct
Site
More than Long
twice
term
Moderate
Moderate
Probable
Moderate
High
Indirect/
Direct
Site
More than Long
twice
term
Moderate
Moderate
Probable
Moderate
High
Site
More than Long
twice
term
Moderate
Moderate
Probable
Moderate
High
Improved local Economy
Impacts on the local Indirect/
Site
due
to Direct
Preparation economy
alternative
income
and
Operational generating activities,
increased employment
levels, influx of people
to the area, land use
changes,
increased
purchasing power.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Increased Social Interaction
Operational The project will offer Direct
variety
of
social
amenities
Impacts on Localised Soil
Loss of organic matter Direct
Site
nutrients
by
Preparation and
removal of top soil and
and
overburden. May result
Operation
in soil erosion
ROSINVEST -EIS
Site
More than Medium
twice
term
Moderate
Moderate
Probable
Moderate
High
Local
Once
Low
Moderate
Unlikely
Moderate
Moderate
Local
More than Long
twice
term
Moderate
Moderate
Probable
Moderate
low
Local
More than Short
twice
term
Moderate
Moderate
Possible
Moderate
Moderate
Site
More than Short
twice
term
Low
Low
Probable
Moderate
Moderate
Medium
term
Impacts on Water Quality
Site
Operation
Siltation
of
water Indirect
courses due to soil
erosion from mining
activities.
Impacts on Air Quality
Temporary
air Direct
Site
pollution due to dust
Operation
generated
by
excavation,
vehicle
traffic
and
transportation
of
materials and fumes
from vehicles and
equipment
Impacts on Noise
Noise generated by Direct
Site
mining
activities,
Operation
especially
vehicles,
earthmoving
equipment, excavation
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
of
construction
materials and Blasting
Impacts of Traffic
Mining activities could Indirect
Site
impact on undisturbed
Operation
areas in the proposed
mining area.
Increased noise levels.
Indirect
Impacts of Occupation Health and Safety
Lack of safety and Direct
Site
regulations
Preparation health
could
impact
and
negatively
on
the
Operation
mining workers.
Operation
Workers could be in Direct
danger of accidents
from machinery such
as excavators etc.
Local
Once
Site
Medium
term
Moderate
Moderate
Probable
Moderate
Low
More than Long
twice
term
Moderate
Low
Possible
Low
Low
Site
Once
Moderate
Moderate
Possible
Low
Moderate
Site
More than Medium
twice
High
Moderate
Possible
Moderate
Moderate
Short
term
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
7.0
ROSINVEST -EIS
ENVIRONMENTAL MANAGEMENT AND MONITORING PLAN
This Section presents the environmental management and monitoring plan. The plan shall be
audited annually to assess compliance and non-compliances shall be highlighted to management
for taking actions.
To successfully implement commitments presented in this report and specifically in this Section,
the Environmental Management Reporting structure below is hereby proposed. The Safety,
Health, Environmental and Social Manager (SHES) shall be appointed and this person shall be
responsible for coordinating all environmental and social activities. The Mine Manager is in
Charge of the Mine and Manager SHES shall report to him. A variety of alternatives, such as the
following, exist for the design and management of the project:
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Table 20:No.
Environmental Management and Monitoring Plan (EMMP) and Cost Estimates
Management and
Monitoring
Objectives
1.0 Positive Impacts of the Project
Impacts or Aspects
Job creation
1.2
ROSINVEST -EIS
Creation of business
opportunities to
locals
1.3
Increase
to
the
government revenue base
through tax
1.4
Increase
to
the
government revenue base
through tax
1.5
Profit to the company for
reinvestment
1.6
Increased
corporate
Management Activities or
Mitigation Measures
Monitoring
Indicators
To ensure that first
priority is given to
the local people
especially for nonspecialized jobs
All recruitments shall be advertised
in the local community and a
database shall be developed for
available local people with special
skills
Number of locals employed
against the number of foreign
employees
Bi-annual
To facilitate local
participation
in
business
opportunities created
by Rosinvest (Z)
Limited
To align the mine
development
in
accordance
with
government policy on
large
scale
development
of
mines
To ensure that all the
revenue
due
to
government and the
Local Authority is
remitted
Local business especially relating
to daily consumables required at the
mine shall be promoted. Examples
include garden and poultry produce.
First priority shall be given to local
suppliers
Top mine management shall remain
committed to the Large Scale
Miners Association of Zambia and
shall continue providing the
necessary support
Number of local businesses
supported by the mine
Bi-annual
Active participation in the
Association of Large Scale
Miners
Bi-annual
The company operations shall
remain open to external auditors
and
professional
accounting
systems shall continue being
applied to ensure that all the forms
of tax due to government and the
Local Authority is remitted.
The holding company shall
continue identifying opportunities
for reinvestment especially in the
mining industry to ensure that the
profit realized is shared with other
Zambians.
All contribution to the community
Total tax paid to government
per annum
Annual
General
Manager/Director
(to be done by an
independent
person)
10,000
Number
of
investments
undertaken or planned to be
Undertaken within Zambia as
part of reinvestment
Annual
General
Manager/Director
(to be done by an
independent
person)
15,000
Number of corporate social
Bi-annual
General
20,000
To operate the mine
in a profitable
manner so much that
the company can reinvest and expand in
Zambia
To formalize the
154
Monitoring
Frequency
Responsible
personnel
General
Manager/Mine
Manager (to
done
by
independent
person)
Mine
Manager/SHES
Manager (to
done
by
independent
person)
General
Manager/Mine
Manager
Annual
Monitoring
Cost (ZMK)
10,000
be
an
20,000
be
an
N/A
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
social
responsibility
especially in beekeeping
activities,
malaria
control,
conservation
farming, health and
education.
corporate
social
responsibility
and
implement activities
in
a
systematic
manner and avoid
duplicity of effort by
other institutions.
ROSINVEST -EIS
shall be documented and publicized
The Kalomo District Development
Coordinating Committee (DDCC)
shall always be consulted for any
community development activity of
significance
responsibility
activities
undertaken per year
Manager/SHES
Manager (to be
done
by
an
independent
person)
To
ensure
that
workers
have
reasonable time with
their families
The work schedule shall
formulated maintained and
workers shall be reminded to
go home when on break
be
Number of weekends taken
off and leave days taken per
employee
Quarterly
To strengthen family
ties
and
avoid
creating room for
marital problems
Professional counseling services
shall be offered
Number
of
complaints
recorded
from
family
members and spouses
Quarterly
A grievance mechanism shall be
developed within Six (6) months
following approval of this report
and this shall guide management of
all related grievances.
Number of grievances and/or
litigations recorded regarding
land use and mining rights
Monthly
Mine
Manager/SHES
Manager (to be
done
by
an
independent
consultant)
Same as above
Number
of
grievances
recorded
Regarding recruitment of
local people
Monthly
Mine
Manager/SHES
Manager
Covered in the
cost above
Same as above
Number of cases of trespass
and
Encroachment recorded by
security personnel
Monthly
Assistant
Mine
Manager/Security
Manager
Covered in the
cost above
Same as above
Number
of
negative
comments about the project
officially submitted
Monthly
Mine
Manager/SHES
Manager
Covered in the
cost above
2.0 Social Challenges for Employees
2.1
2.2
Weakness in the family
structure as a result of
spending Five (5) days
every week away from
the family
Risk of marriage breakup and marital problems
General
Manager/Mine
Manager/Human
Resources
Manager
General
Manager/Mine
Manager/Human
Resources
Manager
5,500
5,500
3.0 Conflicts with the Community
3.1
Land use and mining
rights conflicts
3.2
Recruitment related
Conflicts
3.3
Encroachment
Trespass
3.4
Negative perception by
the community towards
the project
and
To amicably solve
mining rights and
surface rights issues
that
may
arise
without
disadvantaging
anyone
To give first priority
to the local people
and
ensure
zero
tolerance to labor
exploitation.
To protect flora and
fauna resources in the
mining surface area
by
preventing
trespass and
encroachment
To create a good and
transparent
relationship with the
155
60,000
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Discrimination
community
and
prevent a hostile
perception towards
the mine by the local
people.
To give an equal
opportunity to all the
employees including
those living with
HIV/AIDS
ROSINVEST -EIS
Same as above
Number
of
complaints
submitted to management
regarding discrimination
Annual
General
Manager/Human
Resources
Manager
10,000
Number
of
employees
submitted
complaints to the Human
resources
department
regarding
stigmatization
Number
of
complaints
submitted to management
regarding discrimination
Annual
General
Manager/Human
Resources
Manager
15,000
Annual
General
Manager/Human
Resources
Manager
15,000
Volume of waste material
used for backfilling purposes.
The number of progressive
rehabilitation
activities
conducted per year. Number
and type of trees and grass
planted
as
part
of
rehabilitation activities. The
progressive
rehabilitation
budget spent per year shall
also be considered.
Total area cleared compared
with the mine licence area.
Volume
of
overburden
disposed off. Volume of raw
material transported to the
washing plant and the volume
Annual
Mine
Manager/SHES
Manager
2,500
Annual
SHES Manager
2,500
4.0 HIV/AIDS Related Challenges
4.1
Stigmatization
To treat employees
living
with
HIV/AIDS equally
especially with other
employees
Equal opportunities shall be given,
discrimination shall not be tolerated
and professional counselors shall be
engaged to offer counseling and
voluntary testing services
4.2
Discrimination
To give an equal
opportunity to all the
employees including
those living with
HIV/AIDS
Same as above
5.0 Change of Landscape and Land Degradation
5.1
Loss of the natural
aesthetic value due to
opening up of the
area and mining waste
disposal
To try and restore the
natural built of the
area by implementing
progressive
rehabilitation
activities.
Progressive rehabilitation shall
be introduced and once production
starts, backfilling of the pit with
waste rock shall also commence
5.2
Loss of
land use
potential due to mining
waste disposal and the
open pit development
To minimize land
clearing and to ensure
that all forms of
waste are
disposed
of
in
accordance with the
Same as above
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
5.3
Hazardous
and
nonhazardous waste
generation and disposal
Zambian legal
Provisions
To attain maximum
adherence to the
hazardous and nonhazardous
waste
management
Regulations
ROSINVEST -EIS
of the pit.
All the hazardous waste and nonhazardous waste shall be managed
in accordance with respective
Regulations.
Quantities and types of
hazardous waste generated
and disposed off. Area of land
contaminated by hazardous
waste
Monthly
SHES Manager
5,000
Mine
Manager/SHES
Manager
Consultants
(TEME)
Mine
Manager/SHES
Manager
90,000
6.0 Occupational Health and Safety
6.1
Exposure to dust causing
silicosis
To minimize dust
emissions and protect
all
employees
exposed to dust
Periodic monitoring of ambient,
safety induction, medical checkups, dust suppression and provision
of protective clothes
Medical reports, ambient dust
levels and number of dust
protective clothes issued to
employees
Annual
6.2
Explosion risk from
explosives and fly-of
rocks from blasting
To avoid possible
accidents due to poor
handling
of
explosives
Number of accidents and near
misses recorded
Monthly
6.3
Bodily injury due to
misuse of machines and
accidents
To
minimize
accidents and near
misses arising from
usage of machinery
Number of accidents and near
misses recorded
Monthly
Mine
Manager/SHES
Manager
N/A
6.4
Road traffic Accidents
To minimize possible
road traffic
accidents by adhering
to traffic control
standards
and
procedures
Number of accidents and near
misses recorded
Monthly
Mine
Manager/SHES
Manager
N/A
6.5
Open pit or dump wall
collapsing
To conduct mining
and overburden
disposal in a
standard and
professional manner
Only blasting licence holders shall
handle explosive, the blasting
schedule shall remain at 16:00 hrs
and access to the pit shall be highly
restricted
Periodic safety talks shall be
conducted, safety statistics shall be
published, safety inductions shall
be compulsory and safety observes
shall be appointed.
Traffic signs and humps shall be
installed not only for the access
road to the mine but including other
public roads used to access the
mine site. All drivers shall be
reminded of the dangers associated
with careless driving and road
traffic offences shall not be
acceptable
The pit shall be developed in
accordance with the pit design and
a qualified Mining Engineer shall
always be responsible for mining.
Supervised end-tipping shall be
strictly followed and the dump shall
be managed and developed
Number of tension cracks
around
the
pit
and
Overburden Dump, accidents
and near misses and number
of rock/earth fall recorded
Monthly
Mine
Manager/SHES
Manager
N/A
157
N/A
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
according to the proposed design
and conditions that shall be
prescribed by the Mine Safety
Department (MSD)
7.0 Air Pollution and Air Quality Monitoring
7.1
Dust emission from the
pit, waste dumps and
access roads
To minimize ambient
dust pollution by
monitoring and dust
suppression activities
7.2
Exhaust fumes from
generators and heavy
mobile machines
7.3
Workplace air Quality
To minimize air
pollution as a result
of exhaust fumes by
periodic servicing of
machinery
To protect employees
working in confined
areas
from
air
pollutants
Water shall be used for dust
suppression, protective clothes shall
be provided, medical check-ups
shall be done annually and ambient
dust monitoring shall be conducted
The machinery shall be serviced
according to the manufacture‟s
specifications and schedule.
Ambient air quality results
Monthly
SHES Manager
Consultants
(TEME)
130,000
Conformance
with
servicing schedule
the
Monthly
SHES Manager
N/A
Air quality monitoring at various
benches within the open pit at the
overburden
dump
shall
be
conducted monthly to ensure that
siliceous dust is below the statutory
allowable concentration of 350
parts per cubic centimeter. Dust
masks shall also e provided to all
employees and it shall be
mandatory to use them when
working in the pit or at the
overburden dump.
Monthly
siliceous
concentration results
dust
Monthly
SHES
Manager/Mine
Manager
Consultants
(TEME)
All forms of hazardous waste shall
be recorded. Generation and storage
shall be in designated facilities and
transportation and disposal shall be
done by registered companies.
Spillage containment facilities shall
always be available at points where
hydrocarbon wastes shall be
generated. All employees shall
undergo environmental induction
Waste bins shall be provided for the
kitchen and offices and these shall
Quantities and types of
hazardous waste generated
and disposed of.
Presence of generation and
storage facilities. Evidence of
necessary
Licenses
Monthly
SHES Manager
N/A
Quantities of domestic waste
generated and disposed off.
Monthly
SHES Manager
N/A
15,000
8.0 Water and Soil Pollution
8.1
Hazardous
waste
generation and disposal
To prevent soil and
water pollution by
proper
generation,
storage and disposal
of hazardous waste
8.2
Domestic waste Disposal
To prevent water and
soil pollution by safe
158
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
disposal of domestic
waste
8.3
Sewage disposal
To
ensure
that
sewage from the
camp is disposed off
in a nonpolluting
manner
8.4
Effluent generation and
disposal
To attain maximum
adherence to the
effluent standards as
enshrined to the
Water Pollution
Regulations
ROSINVEST -EIS
always be provided with bin-liners.
Littering shall not be acceptable
and reminder signs shall be
installed to inform workers and
visitors that all domestic waste
must be thrown in designated waste
bins. The waste shall be disposed
through a landfill which shall be
licensed with ZEMA. Records of
the waste disposed off per week
shall be maintained.
Septic tanks shall be constructed
with a soak-away system which
shall be used for domestic waste
water such as water from the
laundry as this may affect
biological activities if disposed off
through the modular sewage
management system
Perimeter silt traps shall be
constructed. All the open pit water
shall be pumped into a settling
pond before discharge. The
discharged effluent shall be
frequently monitored.
Adherence to good practices
at the landfill (fenced,
warning signed, waste back
buried with top soil, and
facility under lock-and key).
Presence of the modular
sewage treatment facility and
the level of biological
parameters in the effluent
Monthly
SHES Manager
N/A
Weekly field results for pH,
Conductivity,
Dissolved
Oxygen and Total Dissolved
Solids. Quarterly results for
physical, chemical, total
hydrocarbons and biological
parameters as analyzed by a
reputable laboratory
Weekly
for
field
parameters
and
quarterly for
lab
analysis
SHES Manager
Consultants
(TEME)
50,000
Noise
monitoring
shall
be
conducted frequently and controlled
blasting shall be applied
Noise results
Monthly
SHES Manager
Consultants
(TEME)
15,000
Same as above
Noise results
Monthly
SHES Manager
N/A
Noise monitoring shall be done
monthly and where noise levels
exceed the international threshold
Noise results
Monthly
SHES
Manager/Mine
Manager
N/A
9.0 Noise and Vibration
9.1
Blasting activities
9.2
Haulage of material and
operations
of
the
generator
9.4
Workplace
Monitoring
noise
To minimize noise
and vibration by
using the right type
of explosives
To reduce the noise
emanating
from
haulage tracks by
having the machines
frequently serviced
To protect human
Health
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
limit value of 85 dBA, use of ear
muffles shall be mandatory and
warning signs shall be provided
10.0Loss of Flora and Fauna
10.1
Loss of flora due to
project
related
site
clearing activities
10.2
Deforestation due to
charcoal burning and
encroachment
10.3
Pit and
extension
dump
To reduce the extent
of land cleared for
the pit extension
10.4
Poaching and purchase
of illegal game meat by
employees
To avoid promoting
poaching
and
indiscriminate killing
of wild fauna.
10.5
Weather
To collect climatic
information for
reporting purposes
and use in day-today
operations
OB
To ensure that site
clearing for project
related activities is
limited to the area
required for such
developments only
To protect forest
resources
in
the
mining licensed area
by
preventing
trespass
and
encroachment
Bio-monitoring shall be conducted
annually to determine loss of
vegetation. All site clearing
activities shall be approved by the
Safety, Health and Environmental
Manager.
No charcoal burning shall be
allowed. Security patrols shall be
implemented around the mine area
to control deforestation. Awareness
campaigns shall be conducted
by the Safety, Health and
Environmental Manager.
Vegetation clearing for the pit and
dumpsite shall be limited to
designated areas. The overburden
dump shall be vegetated as a way of
replacing vegetation loss
Being in possession of illegal game
meat or killing of any wild animal
shall be a dismissal offence. Buying
of illegal game meat will not be
acceptable. Awareness regarding
this issue shall be
conducted for all employees
N/A
Total Cost
Area cleared within the mine
licence and density/diversity
of trees preserved
Annual
SHES Manager
Consultants
(TEME)
8,000
Density of forest cover,
number of charcoal kilns,
cases of encroachment
Annual
SHES Manager
N/A
Area covered by the pit and
overburden dump
Monthly
SHES Manager
N/A
Number of offences recorded
Monthly
SHES Manager
N/A
Rainfall
information,
temperature
information,
number of rainy days in the
year, humidity, wind speed
and direction.
Daily
SHE Manager
Consultants
(TEME)
5,000
509,000
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7.1
ROSINVEST -EIS
INSTITUTIONAL FRAMEWORK FOR MONITORING, REPORTING AND
SUPERVISION
In order to ensure that the identified environmental issues are addressed throughout the life cycle
of the project there will be need for all key stakeholders to collaborate. The main objective of
this collaborating network is to ensure that mitigation measures outlined in contracts are being
properly implemented by the Project owner. The main responsibilities of the collaborating
network will be to:-
Complement the efforts for continuous monitoring and assessment of the implementation
of the environmental management plan.
Liaise with respective local authorities on environmental issues which may arise during
the operation of the project.
7.1.1
MONITORING ARRANGEMENTS
To avoid deliberate creation of gaps between what actually gets implemented on the ground, the
contracts must spell out the sanctions for non-compliance with mitigation measures.
The developer is to compile an activity Environmental report from the field visits that will form
the basis for assessment of environmental performance.
7.1.2
OPERATIONAL PHASE
The local authority should be responsible for monitoring and management of all indirect impacts
occurring in the project area.
The following table illustrates the different stakeholders and their monitoring responsibilities
and reporting.
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Table 21: Monitoring and Reporting Responsibilities
ZEMA
Overall environmental performance of the Project
Rosinvest Zambia Limited Monitoring the implementation of EMP
Discussions with Project Manager
Regular environmental progress
Overall environmental performance
reports to stakeholders
the Project
Contractor / Project/
Mining Methods and Materials
Regular environmental progress
Site Manager
Implementation of mitigating measures for air, water, odour, etc.
Environmental management of worksites
reports to ZEMA
Incident reports as and when
Develop Waste management Plan
required (Pollution, accidents, etc.)
Rehabilitation of abandoned worksites
by ZEMA, local authority
Performance of equipment
Accidents (rock falls, pollution spills, etc.)
Negative social and environmental impacts
Environmental performance of equipment
Maintenance records
Implementation of mitigating measures
Accidents reports
Occupational health and safety plan
Mitigating actions
Traffic and worksite accidents report
Air quality
Local Authorities
Negative social and environmental impacts
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Complaints to Project Manager
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8.0
ROSINVEST -EIS
CLOSURE AND DECOMMISSIONING
Closure and decommissioning of the Project would be accomplished in accordance with
Zambia‟s Mining and Environmental Guidelines and the Company‟s Policy and Standards.
Reclamation activities would be designed to achieve, at a minimum, post-mining land use
consistent with a level of productivity and biodiversity present at pre-mining levels. Post-mining
land use would be determined in consultation with the ZEMA, other Zambian governmental
institutions and stakeholders and local communities and is likely to include areas for agriculture,
livestock grazing and wildlife habitat.
A detailed Closure and Decommissioning Plan is required to be submitted to the ZEMA. The
Closure and Decommissioning Plan would describe reclamation objectives and specific
reclamation/closure activities for the open pits, Waste Rock Disposal Facility, Tailings Storage
Facility, Water Storage Facility, Crushing, Washing and Process Plant, Sediment Control
Structures, storm water management structures and ancillary facilities. Final grading and
contouring schemes would also be described for the Project area.
The Closure and Decommissioning Plan would be developed for anticipated operational
conditions of facilities, tailings characteristics, site climatic conditions and available construction
materials.
The Closure and Decommissioning Plan would also include descriptions of practices to be
implemented for post-operational water management and for ensuring long-term stability of
reclaimed areas.
The Company‟s broad reclamation objective for the Proposed Mining Area is to ensure that the
site is left in a condition that is safe and stable, long-term environmental impacts are minimised
and any future liability to the community and future land use restrictions are minimised.
Specific Reclamation Objectives to be included in the Closure and Decommissioning Plan
include:
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Legal Compliance - Meet all statutory requirements.
Landform Stability - Ensure that land is left in a stable condition that minimises longterm environmental impacts and does not compromise proposed post mining land uses.
Eco-system Re-establishment - Reclaiming as much of the affected area as possible to a
condition where its pre-mining usage can resume and ensuring the eco-system function is
representative of this land-use. The primary pre-mining uses include cropland, livestock
grazing and small residential development.
Water Quality- Ensure that the quality of water that discharges from the reclaimed mine
area meets standards for the immediate downstream use.
Public Safety - Ensure that reclaimed land is physically safe for people to access and
does not pose a human health risk.
Infrastructure – Decontaminate, decommission, salvage or demolish all structures on the
site according to the terms of the mining agreement. These include facilities, ancillary
equipment and buildings.
Biodiversity – Ensure that the biodiversity of the Proposed Mining Area is maintained at
pre-disturbance levels or improves.
The Company has prepared a Provisional Land Rehabilitation Plan that addresses land
stabilization and erosion controls during the life span of the mine. The Company proposes to
optimize this provisional plan to address the land stabilization and erosion control issues
associated with the broader Project
Notwithstanding the outcome of processes to arrive at a more detailed and sustainable Closure
and Decommissioning Plan and Land Rehabilitation Plan, this section of the EIS provides a
framework for the closure and decommissioning approach for the Project.
8.1
GENERAL APPROACH
Short-term reclamation goals would be to stabilize disturbed areas and protect disturbed and
adjacent undisturbed areas from unnecessary or undue degradation by erosion or sediment
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transport and deposition. Long-term reclamation goals would be to ensure public safety, stabilise
the site and establish a productive vegetative community consistent with specific and targeted
post-mine land uses and in line with the EMA reclamation success criteria. The Company‟s
priority is to decommission and reclaim the Proposed Mining Area in a manner that is protective
of human health and the environment, to the maximum extent practicable. General reclamation
activities would include the following:
Contour the surface of the Tailings Storage Facility,
Place a portion of the waste rock in the open pit,
Contour the surface of the Waste Rock Disposal Facility,
Regrade roads,
Complete grading to ensure adequate drainage control,
Remove and regrade stockpile areas,
Replace salvaged topsoil,
Seed disturbed areas and
Monitor reclamation success.
Reclamation activities would be progressively completed during the operational phase of the
Project as specific areas or facilities would no longer be needed to support operation, and the
activities would continue for approximately two years after mining ceases.
Upon completion of reclamation and decommissioning activities, the site would be subject to
post-closure monitoring. Post-closure monitoring would continue after the reclamation phase of
the Project until such time as all closure objectives and success criteria defined in the final
approved closure plan have been met.
8.2
RECLAMATION ACTIVITIES
Several reclamation actions would take place prior to, during and following mine development
activities within the Proposed Mining Area. These actions are described below.
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8.2.1
ROSINVEST -EIS
TOPSOIL SALVAGE
As the mine, haul and access roads, stockpiles, Waste Rock Disposal and Tailings Storage
Facilities are being constructed; the Company would recover available topsoil from these sites
for future use in reclaiming disturbed areas. Topsoil profiles vary considerably across the
Proposed Mining Area. Recovery depths would be determined through an analysis of soil data
collected during baseline studies of the Study Area as verified by on-the-ground reclamation
specialists during salvage operations. The overall intent is to obtain only the growth medium
(topsoil and subsoil) necessary to achieve the objectives of the Closure and Decommissioning
Plan. Topsoil would be salvaged and transported to stockpiles using scrapers, wheel and track
dozers, haul trucks and loaders. Subsoil materials, where suitable for use as growth media in
reclamation, would be salvaged and stockpiled separately from topsoil.
8.2.2
GRADING DISTURBED AREAS
Prior to replacing topsoil or suitable growth media, facility sites and other disturbed areas would
be graded to attain a stable configuration establish effective drainage, minimise erosion and
protect surface water resources. To the extent practicable, grading would blend topography of
disturbed areas with the surrounding natural terrain.
Angular features, including tops and edges of the Waste Rock Disposal Facility, would be
rounded.
8.2.3
REVEGETATION
Prior to initiating the proposed reclamation vegetation plan, the Company would evaluate topsoil
replacement depths for various exposures to arrive at a design that accounts for soil replacement
depths that may vary according to location and soil type. The variety of replacement depths
would provide different vegetation mosaics on reclaimed areas. The regraded surface would be
ripped where necessary prior to placement of topsoil. Ripping would reduce compaction,
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maximise infiltration, provide a uniform seed bed and establish a bond between subsoil and
topsoil. The Company‟s re-vegetation programme goals would be to stabilize reclaimed areas,
ensure public safety and establish a productive vegetative cover based on applicable land use
plans and designated post-mining land uses.
8.3
CLOSURE AND DECOMMISSIONING OF MINE
COMPONENTS
Using methods described above, decommissioning and reclamation of the major components
associated with the Project would occur as described below. Variations to these general
descriptions, up to including salvaging much of the infrastructure associated with these facilities,
would occur in the event the outcome of the process that engages stakeholders in developing a
sustainable land rehabilitation plan for the Project indicates otherwise. The Closure and
Decommissioning Plan envisioned represents a more traditional approach to site closure.
8.3.1
OPEN PIT
The open pit would cause a change in land form in the Proposed Mining Area which would be
considerably different from current topography. As indicated previously, the Company would
concurrently place waste rock in the smaller lobe of the open pit and complete reclamation
during mine operation.
The surface of the waste rock placed in the open pit would be stabilized and sloped to promote
positive drainage, covered with a growth medium and re-vegetated in accordance with the
Closure and Decommissioning Plan. The slope of the reclaimed area trending into the open pit
would be stabilized but would remain relatively steep. Access to the rim of the reclaimed area
would be limited to ensure public safety is maintained until the pit lake forms.
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8.3.2
ROSINVEST -EIS
WASTE ROCK DISPOSAL FACILITY
Following placement of waste rock in the open pit, the remaining waste rock in the Waste Rock
Disposal Facility would be graded and recon toured to provide a minimum 3.0H: 1.0V reclaimed
slope.
Grading would minimise potential for slope failures or rill erosion, facilitate reclamation
activities (seeding, mulching), and provide a surface that would enhance water retention and
support vegetation. The top of the Waste Rock Disposal Facility and remaining safety benches
would be graded to promote runoff of water (free draining), prevent ponding or impounding of
water and limit erosion.
Waste rock would be graded and ripped to relieve compaction from mining equipment. Upon
completion of grading, the Company would redistribute topsoil or other suitable growth media
over the waste rock. The area would then be seeded according to the Closure and
Decommissioning Plan.
8.3.3
ORE STOCKPILE
Generally, ore stockpiles would be removed by the end of mine life and stockpile areas
reclaimed by grading and re-vegetating to blend with surrounding topography. Ore stockpiles
that are not treated during the life of the project would be reclaimed using methods as described
for the Waste Rock Disposal Facility.
8.3.4
PLANT SITE
The mill and process plant would be decommissioned prior to demolition or salvage of any
structures. Portable equipment of value including vehicles, furniture and computers would be
removed for subsequent reuse or salvage. Decommissioning the crushing and washing plant
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would be initiated once the last ore has been processed. The Crushing plant would be
decommissioned once all economic recoverable tin solution has been processed.
Contaminated soil from oil spills and lubricants would also be removed and placed in an
approved disposal facility. Stripped areas in the vicinity of the mill and process plant would be
scarified, covered with topsoil, graded to match contours of surrounding topography and revegetated.
8.3.5
TAILINGS STORAGE FACILITY
Reclamation of the Tailings Storage Facility would commence upon termination of tailings
deposition. After removal of the pond (through evaporation or direct discharge, depending on the
quality and timing of the action) in the low area adjacent to the final spillway, the tailings surface
would be allowed to dry to the point where cover placement is possible without excessive
deformation of the tailings surface. Drying is expected to take approximately 12 months in the
decant/final spillway area followed by installation of a cap during the dry season.
Tailings would be drained via the under-drain system. The under-drain system installed
throughout the tailings basin serves to reduce the phreatic surface within the tailings. Drains
would report to a collection sump, which would be dewatered by pumping from an access riser
pipe. Water treatment may be required during the dewatering process to ensure that water from
the facility can be discharged in accordance with applicable standards. Water quality monitoring
of the seepage and treated effluent would be conducted during the closure period until such time
as seepage meets discharge criteria or until seepage ceases.
The primary focus of reclamation would be revegetation, erosion control and storm water
management. The final profile of the tailings surface would slope from the north, east and west
embankments toward the final spillway. The low point on the tailings surface would be adjacent
to the spillway so that reshaping of the tailings surface would be minimized. The capping
material type and configuration would be determined during detailed design of the closure plan
for the facility.
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8.3.6
ROSINVEST -EIS
WATER STORAGE FACILITY
The Water Storage Facility would either remain as the responsibility of operations and
maintenance, given to an appropriate institution or breached and reclaimed, depending on the
approved Closure and Decommissioning Plan. Maintaining the facility may be useful for the
local community as a source of water for a variety of applications. Ongoing maintenance of the
dam and outlets would be required as well as the source water system that would maintain a
desired pool elevation.
In the event that the approved Closure and Decommissioning plan requires removal of this
facility, an engineered dewatering process would be developed to either direct the water into the
downstream drainage (depending on water quality) or into the open pit. The dam creating the
reservoir would be removed with material to be used for reclamation cover material (if suitable)
or hauled to the waste rock disposal facility prior to reclaiming those sites. The impoundment
area would be allowed to dry and the resultant land surface would be scarified, shaped to blend
in with surrounding topography, covered with suitable growth media and re-vegetated.
8.3.7
SEDIMENT CONTROL STRUCTURES
Upon completion of closure and reclamation activities, accumulated sediment would be removed
from areas upstream of the sediment control dams. Where possible, sediment and topsoil
collected from the base of the sediment control structures would be redistributed in areas
requiring additional reclamation growth media. The sediment control structures would then be
breached to restore free flowing conditions and the area reshaped to blend with the surrounding
topography.
8.3.8
ROADS
Roads associated with the Project would be reclaimed concurrently with cessation of operations
in each individual area. Roads remaining at the end of mining operations would be reclaimed
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when no longer needed for reclamation and/or monitoring access. Reclamation of haul roads
would be by grading to provide proper drainage, replacement of topsoil and revegetation.
Reclaimed roads would be graded, to the extent practical, to re-establish the original topography
and drainage of the site in order to minimise erosion. Haul roads associated with the waste rock
disposal facility would be reclaimed concurrently with closure of the disposal site.
Exploration roads, drill pads, sumps and trenches would be reclaimed in conjunction with
ongoing operations. Exploration roads are constructed by stripping topsoil and using the topsoil
as a safety berm at the edge of the exploration road. Topsoil in the berm would be redistributed
back onto the graded surface during reclamation.
8.3.9
ANCILLARY FACILITIES
At the end of the Project mine life, the explosives magazine would be removed in consultation
with the MSD and fuel tanks and other mine support structures with significant salvage value
would be dismantled for salvage or used for other operations in the area. Unused explosives
would be returned to the vendor or used at other mine sites. Some Project facilities, such as the
accommodation and administration structures, may be turned over to an agreed upon end user or
may be dismantled at the government‟s discretion.
8.4
MONITORING
Procedures for short- and long-term monitoring of the Proposed Mining Area after closure would
be established as a continuation of the operational monitoring programme to ensure that mining
activities do not affect surrounding areas. The items scheduled to be monitored should not be
considered as an all-inclusive monitoring list, and would be updated as mining and reclamation
activities progress. Periodic environmental reporting would be undertaken as required by the
appropriate statutory authorities.
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Short-term monitoring would consist of monthly monitoring of groundwater, fugitive dust,
revegetation progress, surface water run off quantity and quality, open pit condition, pit lake
water quality and Waste Rock Disposal Facility and Tailings Storage Facility effluent quantity
and quality. Monitoring would be performed routinely for the life of the Project. Monitoring
groundwater, surface water and pit lake water would consist of sampling for a selected list of
parameters. Air monitoring stations would be installed and sampled for fugitive dust.
Revegetation would be inspected for erosion, biodiversity and growth.
Long-term monitoring would be conducted on a quarterly basis and would consist of a
combination of observations, well measurements and sampling for water and air quality.
Groundwater and surface water sampling and site observations would be conducted in
accordance with a schedule agreed upon in discussions with the appropriate agencies.
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Table 22:- Decommissioning and Closure Activities and Cost Estimates
Project Facility
Activity
Responsible
Cost (K)
Organisation/Personnel
Direct Costs
Open Pit
Groundwater filling of open pit; construct spillway and decant
Developer/Site Manager
80,000
Reshaping/topsoil placement of selected areas(1), establish Developer/Site Manager
45,000
System; grade and place topsoil on selected areas; establish
erosion control vegetation; establish initial soil stabilizing and
nitrogen fixing vegetation; establish final land use vegetation on
selected areas.
Total Waste Rock Disposal Facility
erosion control vegetation – slopes, tops, and benches, establish
initial soil stabilization and nitrogen fixing vegetation, establish
final land use vegetation
ROM Zone
Reshaping, topsoil and growth media placement, establish Developer/Site Manager
15,000
erosion control vegetation, establish initial soil stabilizing and
nitrogen fixing vegetation, establish final land use vegetation
Plant Site
Demolition and removal of treatment plant, structures, concrete
(Treatment plant; Mine Services; footings; backfill foundation areas; removal of affected soil; reExplosives Magazine)
spreading of topsoil/overburden; establish erosion control
vegetation (flat surface); establish initial soil stabilizing and
173
Developer/Site Manager
20,000
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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nitrogen fixing vegetation; establish final land use vegetation.
Haul & Access Roads
Rip and grade, place topsoil in selected areas, establish erosion Developer/Site Manager
25,000
control vegetation, establish initial soil stabilizing and nitrogen
fixing vegetation, establish final land use vegetation
Sediment Control Structures and Remove sediment – place on reclaimed areas ; remove and Developer/Site Manager
Process Water Ponds
18,000
dispose of liner; rip and grade compacted surfaces; replace
growth media on selected areas; establish erosion control
vegetation; establish initial soil stabilizing vegetation and
nitrogen fixing vegetation; establish final land use vegetation.
Tailings Storage Facility Area
Reclaim oxide waste from dump, truck, and place & spread Developer/Site Manager
8,000
topsoil; final grading for water management; water treatment as
necessary; establish erosion control vegetation; establish initial
soil stabilizing and nitrogen fixing vegetation; establish final
land use vegetation.
Sub Total
211, 000
Indirect Costs
Mobilization and Demobilization
Developer/Site Manager
12,000
Developer/Site Manager/Consultant
10,000
Management
Developer/Site Manager
50,000
Repairs and Maintenance
Developer/Site Manager
50,000
Developer/Site Manager/Consultant
60,000
Consulting services
Monitoring/Decommission Report
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Sub Total
ROSINVEST -EIS
180, 000
Grand Total
391, 000
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9.0
CONCLUSION AND RECOMMENDATIONS
9.1
FINDINGS OF THE EIA
ROSINVEST -EIS
The proposed Rosinvest Zambia Limited Mine is located within the Southern Province, and
within the Kalomo District Municipality. The study area is underlain by the Tin deposits.
Activities in the surrounding areas include mining activities as well as farming.
The proposed mine will be developed on a land constituting a total area of approximately 40km2.
The site is previously undisturbed with activities consisting of a combination of vacant,
wilderness land and subsistence farming. Sensitive areas were identified prior to the
development and conceptual design of the mine layout, which therefore takes cognisance of the
environmental sensitivities of the study area.
The main impacts associated with the development include impacts on the groundwater,
including seepage from the tailings dam and dewatering of the mine. Impacts on the air quality
are significant without mitigation measures; however, with the implementation of appropriate
mitigation measures as outlined in this report, the impact significance is reduced to “low”.
Impacts on the terrestrial ecology are significant and have a rating of “medium” for the loss of
vegetation of medium ecological importance, as well as fragmentation of natural habitat. Other
impacts assessed include impacts on the aquatic ecology of the Chirobi area, impact on soils,
noise, heritage resources, visual and impacts on health and social wellbeing.
9.2
RECOMMENDATIONS
The mitigation measures proposed by the specialists were incorporated into the Environmental
Management and Monitoring Programme (EMMP) and must be adhered to by the mine.
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Roles and responsibilities were assigned to each mitigation measure. Monitoring will take place
for the groundwater and atmospheric emissions. Monitoring measures are included in the
EMMP.
It is recommended that an Environmental Management System is developed by the mine, which
should be incompliance with ISO14001. The mine should aim to acquire ISO14001
accreditation.
9.3
CONCLUSION
It is recommended that the mine is authorised to proceed for the following reasons:
The new mine will be located in an existing mining region and therefore will not induce
an unexpected disruption to the social environment.
The mine will be located outside of areas of environmental. However, vast expanses of
the vegetation type occur in the surrounding areas, thus in the event that the mine
proceeds, it is anticipated that the impact will be of medium significance.
The impacts of dewatering of the underground aquifer, as well as seepage from the
tailings dam are significant; however, these impacts can be mitigated to a certain extent,
and therefore do not represent fatal flaws.
Other impacts can be mitigated to levels which are acceptable, and therefore will not
have a detrimental impact on the environment.
The proposed mine will induce positive socio-economic impacts within the area and the
Province, which is currently characterised by high levels of unemployment.
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LIST OF ANNEXTURES
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ANNEX 1
ATTENDANCE REGISTER
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181
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182
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ROSINVEST -EIS
ANNEX 2
MINUTES OF THE
SCOOPING MEETING
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MINUTES OF THE SCOOPING MEETING FOR ROSINVEST (Z) LIMITED
TIN MINING PROJECT KALOMO DISTRICT
Date
13th March, 2014,
Venue:
Chirobi Village
Attendance:
See attached schedule
Chairman’s introduction remarks
The Chairman (Mr. John Simumba Director Tropical Environmental Management
Experts (TEME)/Mr. Silungwe interpreter (Rosinvest Zambia) called the meeting to order at
exactly 12:30hrs. He begun by welcoming everyone present at the meeting. He introduced
himself first and then introduced the developer to the gathering. He told the meeting that his
company has been contracted to carry out an Environmental Impact Assessment (EIA) and
prepare an Environmental Impact Statement (EIS) afterwards which will be submitted to the
Zambia Environmental Management Agency for approval of the project before commencement.
He told the meeting that his area of concern is the environment. He said that before any
submission to ZEMA a meeting like this needed to take place so that all views and concerns
regarding the project would be taken into account and incorporated in the document.
Mr. Simumba
Mr. Simumba talked about the environmental part of the project and mentioned that the meeting
was called because the government requires that the public meeting be conducted before
development could take place. He quoted The Environmental Management Act (EMA) No. 12 of
2011 which came into force after repealing the Environmental Protection and Pollution Control
Act (EPPCA) of 1990 cap 204 of the laws of Zambia. This Acts states that the Agency shall
conduct surveys on the state of the environment and research and forecast environmental
changes and undertake other studies that may contribute to the formulation of policies and
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preparation of action plans and strategies with regard to environmental protection, conservation
and management. It also provide for the prevention and control of pollution and environmental
degradation.
He said that in 1997, the EPPCA established regulations for conducting and reviewing of
Environmental Impact Assessments as well as detailing the types of projects that require
Environmental Impact Assessment. Mr. Simumba stated that the project under consideration
came under section 4 of the Second Schedule Regulation7 (2).
He stated that the law required that the developer had to meet certain requirements and also had
to follow them as they were in the document so that environmental impacts on mining would be
minimal.
He also mentioned that there were a lot of things that take place during mining like disturbing the
livelihood of the people, habitat of the area, and noise and air pollution from moving vehicle if
the mining was not done in a controlled way. He retaliated that trees would not be cut
unnecessarily to avoid soil erosion. He pointed out that there will be little disturbance to the ecosystem of the area in order to maintain the habitat.
Mr. Simumba mentioned that as neighbours and stake holders they needed to know what will be
happening and if they had any comments, complaints or questions concerning the project they
would be addressed and there comments would be put in the document that would be produced
as Environmental Impact Statement (EIS).He also mentioned that the EIS document would be
advertised in both the print and electronic media for more than 2 weeks.
He then listed issues that the study will address surrounding the following aspects of the
environment;
Land and soil;
Air quality and noise environment;
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Surface water;
Underground water and quality;
Occupational health and safety;
Public health and safety;
Traffic, road safety and public access;
Local Ecosystem, vegetation and habitat; Land use/ Aesthetics;
Employment and multiplier effects
ROSINVEST -EIS
In conclusion he mentioned the benefits of the project and the development that will be brought
to the area and how as neighbors they would be able to benefit from the project during life cycle
of the project.
Then Mr. Simumba called upon Mr. Banda to outline the Social-Economic Impacts that will
result when the project is implemented.
Social-Economic Impacts outlined by Mr. John Banda
Mr. Banda talked about the social impacts of the project like creation of employment of about 80
people will be employed construction and operation of the mine. He stated that most of the work
will be given to local people. He also talked about the multiplier effects that would come with
the project where other businesses would benefit like suppliers e.g. food suppliers and benefits
that would go to government department like Kalomo District council from collection of levies.
He also mentioned benefits to the insurance industry, Napsa, Workers compensation ZRA and
the banking sector. He mentioned the benefits to local people both skilled and unskilled who
would earn a living during the project implementation phase. He also mentioned that the road
network will improve.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Negative Social Impacts
Mr. Banda also advised the local community to get involved in all project phases and monitor
any irregular conduct by the developer in order to minimise negative impacts of the project.
He also talked about the negative impacts of the project. Since the mine will attracted a lot of
different people he mentioned that diseases such as H.I.V and other STIs would increase. He
outlined how the developer would put up measures to sensitize workers on the dangers of H.I.V
and the frequency of that sensitization that would be at least quarterly in a year.
Views and Comments Session
Mr. Simumba next welcomed questions and comments from the audience.
Question 1
Mr. Sinyangwe a Villager wanted to know what will happen to the fields since the mining area
has been for some time used for mining.
Answer 1
Mr. Simumba responded that it will be upon agreement between the developers/the chief and the
owners of the fields for resettlement.
Question 2
Mr. Marshal asked if the company will help the community in building Schools, Clinics and
Roads.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Answer 2
Mr. Simumba answered by saying that it will be a deliberate policy by the company to help the
community.
Question 3
Mrs. Eness asked the promises from the company.
Answer 3
Mr. Simumba referred to the Social-Economic impacts as highlighted by Mr. Banda.
Mr. Kabonda
Mr. Kabonda wanted to know if the consulting company (TEME) will continue to monitor the
operations of Rosinvest.
Mr. Simumba agreed that the company (TEME) will continue as it will be engaged I monitoring
the management and auditing the company‟s operations (Rosinvest). He also said that other
government institutes such as MSD, ZRA and ZEMA will be visiting the company to monitor its
operations.
Mr. Trust
Mr. Trust recommended the company as it had the consulting company (TEME) representing the
government institute (ZEMA). However he asked if the company will continue helping the
community.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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The Developer Mr. Simukonda assured him that the company will continue helping them as they
will be the company‟s priority.
Mr. Silozi
Mr. Silozi was concerned about the road network since the access road is too small and the pits
left unattended.
The developer said that they will differentiate roads for public and mining equipment.
Mr. Simumba also added that all road networks will have signage e.g. explosives heavy duty
equipment and slow down humps.
He also said that there will be a management and decommissioning plan over the pits and its
cost.
Mr. Gabson/Mary Moonga
Mr. Gabson was concerned about the resettlement since there are squatters within the area.
Mr. Simumba said that it will be agreement between the developer, the chief and the directly
affected people. He also said that the developer will engage the consulting company to do the
resettlement plan.
Mr. Simumba also emphasized that the developer has explored the area and knows the points of
mining area and knows exactly who are within.
Mr. PoiPoi
Mr. PoiPoi wanted to know the area covered by the mine.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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The developer said that the all mine is approximately 20km2.
Remarks from Chief’s Representative Mr. Patrick Champe
Mr. Champe asked if the community welcomed the company to which all agreed. He also told
them that there were lucky as words said by the chief reflecting back that many companies had
cheated them. He asked them if they had seen any difference with Rosinvest to which they said
yes. He highlighted that illegal miners never went to the chief but Rosinvest did. He also said
that the chief agreed with the company that they will build for the community a Dam and a Hand
Pump.
He then called upon the Advisor of the Chief who thanked the community for welcoming the
company and advised the community to avoid theft, vandalism and witchcraft. He highlighted
the benefit the community will derive from the project such as employment, good road network
and public facilities such as schools and clinics.
Conclusion
Mr. Simumba
Mr. Simumba thanked everybody for coming and attending the meeting. He emphasized that the
document will be available for all to see and read.
The meeting came to an end right about 16:00hrs.
Secretary Signature
Chairman Signature
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ANNEX 3
LETTER OF TERMS OF
REFERENCES
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
193
ROSINVEST -EIS
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
ANNEX 4
CVs OF THE EIA TEAM
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
CONTACT DETAILS
31 Kakosa Street Kamenza Township, Chililabombwe
+260 979 505404 or +260 955 098166
moses.kapala@gmail.com
CAREER OVERVIEW
Qualified and experienced Environmental Engineer with broad knowledge in environmental
management. Over two years of energy, environmental and safety management in the mining
industry. I am a Certified auditor and implementer of BSI ISO 14001:2004 Environmental
Management System and internal Safety and quality audits.
PERSONAL ATTRIBUTES
Technically competent/qualified in energy and environmental management.
Calm, reliable and dependable in meeting organisational objectives.
Energetic and physically very fit; quick to respond to opportunities and problems.
Strong planning, organising and monitoring abilities - an efficient time-manager.
Strives for quality and applies process and discipline towards optimising performance
High level computer skills in Microsoft office including Excel, Word, PowerPoint,
publisher, Micro Station Design Software, SAP Business Management Software and
Harrington Quality Management system.
KEY STRENGTHS
Over Two years of experience in development and implementation of ISO 14001
Environmental Management System (EMS).
Identification and development of energy saving opportunities/initiatives to reduce cost.
Over one year of Laboratory and analytical experience and expertise.
Audit skills based on British Standard Institute (BSI).
Lead auditor in internal Environmental and Safety audits and inspection based on the ISO
14001:2004 EMS and OHSAS 18001 SMS.
Designing and conducting Health, Safety, and Environmental management trainings and
awareness.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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CAREER HISTORY
October, 2011 – To present - Environmental Officer-Konkola Copper Mines Plc
Key Responsibilities
Track and report on effluent quality to ensure proactive and timely decision making to
prevent water pollution and increase the efficiency/life of underground pumps.
Ensure 100% closure of BSI ISO14001 Environmental Management System
nonconformities raised to ensure continuous improvement and Certification of the mine.
Assist with the development, maintenance and implementation of environment and safety
standard operating procedures (SOPs) and related plans for mine facilities.
Track and report on energy usage and propose improvement initiatives/corrective actions
to ensure 5% reduction.
Ensure 100% compliance with Zambia Environmental Management Agency (ZEMA)
licence conditions.
Writing Environmental statutory reports to ZEMA and MSD monthly, quarterly, annually
and bi annually for continuous improvement and compliance monitoring.
Coordinating trainings, Environmental awareness and mentoring others in the
implementation of the ISO 14001:2004 and also to meet legislative requirements.
Conducting internal EMS and OHSAS audits and inspections on all the sections of the
mine including suppliers as well as sub-contractors.
Developing environmental aspect/impact registers, Objectives and Targets and
monitoring the implementation of environmental management programs.
Developing scenarios for possible emergence situations and then coordinate emergency
drills i.e. Flooding of the mine and Tailings Dam wall failure.
Coordinate the Investigation of incidents and non-conformances to establish the root
cause and institute corrective action to ensure 100% closure is achieved.
Key Achievements
Improved mine effluent quality by reducing the amount of suspended solid from over
100ppm to less than 65ppm the statutory limit being 100ppm.
Successful implementation and Certification of the mine to the BSI ISO 14001:2004
EMS.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Ensured 98% compliance to ZEMA Licence conditions.
Ensured 100% closures to non-conformances raised during external audits and
achievement of over 90% of the annually set objectives.
January, 2011 – October 2011 – Environmental Engineer (Mine Ventilation)-Konkola
Copper Mines Plc
Key Responsibilities
Emissions sampling from underground machinery and on surface plants to ensure the
levels fall below MSD and ZEMA statutory allowable limits.
Proposing, planning and designing Ventilation systems and set ups using micro-station
software and manually.
Conducting Underground ventilation air flow surveys, smoke shifts and setting re-entry
periods for blasted ends.
Writing ventilation statutory reports to ZEMA and MSD monthly, quarterly, annually and
bi annually.
Coordinating and proposing ventilation emergency preparedness situation by means of
drills in case of an underground gassing incident.
Conducted Occupation Hygiene measurements for Noise and Gas Emissions from the
newly commissioned KCM Diesel Power Plant to assess its impacts in the immediate and
surrounding Environment.
Key Achievements
Effectively designed and implemented a ventilation system at No.1 Shaft 2650‟L by
introducing more fresh air by reopening the Ventilation Shaft VS1D which improved
ventilation conditions by 30%.
Effectively achieved 100% compliance to ZEMA statutory compliance of emissions from
the New Diesel plant by facilitating the approval of sampling procedures.
March, 2010 – December 2010 – Assistant Water Quality/Laboratory Officer (Temporal) Ministry of Mines, Energy and Water Development-Department of Water Affairs (DWA)
HQ
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Key Responsibilities
Water quality sampling of both surface and ground water aquifers to assess the water
quality and pollution levels if any.
Worked hand in hand with Zambia Environmental Management Agency (ZEMA) Staff in
the water sampling campaign of the Kafue River (Lower and upper Kafue River) and
other streams to ascertain environmental pollution levels in Lusaka.
Further laboratory testing and analysis of the collected water samples at the Department
of Water Affairs National Laboratory to quantify compliance to set standards.
Key Achievements
Introduction of new laboratory procedures through research.
Development of an organised record keeping system in the laboratory through document
filling.
EDUCATION AND QUALIFICATIONS
1. Bachelor of Engineering in Environmental Engineering with a major in Combustion and
Energy Engineering with Distinction- Copperbelt University, Kitwe.(2005-09)
1. Examination Council of Zambia School Certificate – Nchelenge Secondary School,
Nchelenge.(2000-02)
2. Examination Council of Zambia Junior Secondary School Leaving Certificate- Mansa
School for Continuing Education, Mansa.(1998-99).
PROFESSIONAL QUALIFICATIONS/DEVELOPMENT
I have undergone various trainings during my graduate training program with KCM and these
include;
BSI Environmental Management System (EMS ISO14001:2004) Internal Auditors
Training.
Occupational Hygiene and Ventilation Controls Certificate Elementary Certificates.
Total Quality Management (TQM) and Harrington Quality Management System
(HQMS) Internal Trainings.
Root Cause Analysis Techniques (RCat) Internal Training.
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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Holder of Clean valid Driver‟s Licence.
Holder of a valid Mining Blasting Licence.
RESEARCH AND PUBLICATIONS
3.
Final year Project: An Evaluation of Water loss in a typical Urban
Distribution SystemA case study of Bulangililo Water Treatment Plant and
Riverside Township Water
Network with NWSC in the year 2009.
4.
Fourth year research project: How the scaling up of Indoor Residue Spray
(IRS) of DDT
in malaria control can be a trade barrier to Zambia.
REFERENCES
1. Mr Mwila Chitoloma
SHE-Environmental Coordinator
Konkola Copper Mines Plc
Konkola Mine, Private Bag KCM (K) 2000,
Chililabombwe, Zambia. Cell: +260 977 844929
E-mail: Mwila.chitoloma@kcm.co.zm
2. Mr Isaac Chongo
Manager – Ventilation
Konkola Copper Mines Plc,
Konkola Mine Private Bag KCM (K) 2000
Chililabombwe, Zambia. Cell: +260 968 338 937
E-mail: isaac.chongo@kcm.co.zm
3. Prof. Nkonde G.K.
Lecturer-Department of Chemical Engineering
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Copperbelt University, Zambia.
P.O. BOX 21692,
Kitwe.
Cell: 0977 879 986.
Email: gnkonde@cbu.ac.zm
200
ROSINVEST -EIS
TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
DOREEN N V MUKUBE
Zambia Institute of Mass Communication Educational Trust
P.O. Box 50386 RW, Lusaka
Mobile: 097 7 859676; 097 7 607225
E-mail: doreennasilelev@yahoo.co.uk
doreen.mukube@gmail.com
PERSONAL INFORMATION
Marital Status:
Nationality:
Date of Birth:
Married
Zambian
January 10, 1980
PROFILE
I am a hardworking, self-motivated individual with great initiative. I am also a self-starter who
is able to handle pressure, achieve results and reach targets. Furthermore, I am a self-starter,
with a mind for corporate image building.
EDUCATION
2012
University of Zambia
Certificate in Project Planning, Monitoring, and Evaluation
2012 University of Wisconsin – Madison Global Health Institute, USA
Certificate in Communicating Public Health Information Effectively
I was trained in communicating health messages effectively and planning communication
strategies pertaining to public health concerns, which included, among other things, writing
letters to the editors, lobbying policymakers, coming up with a testimonial that I delivered
before the representatives of senators in the State Capital of Wisconsin in Madison
This involved researching on particular topics assigned to us and preparing a presentation for a
television interview
2000 – 2004
University of Zambia
Bachelor of Arts, Development Studies & Mass Communication (Major & Minor respectively)
1994 – 1998
Roma Girls Secondary School
General Secondary School Certificate
WORK EXPERIENCE
2011 to date
Zambia Institute of Mass Communication Educational Trust, Lusaka
Specialist - HIV/AIDS (Project Coordinator for the Health Communication Media Project
Funded by USAID)
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
I arrange logistics such as car hire and accommodation for foreign partners
Furthermore, I organise workshops, which involves calling up participants, writing
letters and making budgets for workshops, booking conference halls, and so forth
I have in the recent past organised a DJ‟s training workshop in HIV/AIDS, which was
attended by DJs from several community radio stations
I do the budgeting for the project activities
I write concept papers and project proposals for the proposed activities in the depart ment
and marketing these to prospective sponsors
I preparing work-plans, following through to ensure activities actually take place as
planned
I also carry out monitoring and evaluation of project activities
I write reports and engage in productions of radio and television programmes and
messages on HIV and AIDS
I coordinate meetings for our partners with government officials and other stakeholders
I organise and participate in community outreach activities for the HIV/AIDS project
Public Relations
I arrange for and participate in activities to profile my institution such as participating in
the Agriculture and Commercial Show
I market the courses at ZAMCOM on radio, television and newspapers
I am a consultant for Public Relations for Government Departments
I carry out other Public Relations communications and functions both within and outside
ZAMCOM, in addition to producing materials such as brochures and documentaries for
ZAMCOM
Gender
As the gender focal person at ZAMCOM I lecture on gender and the med ia
I arrange for the students (both pre-service and in-service) to participate in events aimed
at exposing students to gender in the media. Last year I successfully arranged for the pre service students to participate in a cyber-dialogue that was organised by Gender links
and involved students and lecturers from various countries conversing via internet to
mark 16 Days of Activism against Gender Based Violence
Arranged ZAMCOM‟s participation in Women‟s Day activities last year and organised a
ceremony to award an outstanding woman at ZAMCOM
Lecturer
I am a lecturer in Community Development, with a focus on gender issues, community
development, population, and poverty
o This involves preparing notes and lesson plans, maintaining records of students‟
assignments, and organising field trips
These accomplishments are indicative of my abilities to reach audiences with a message
primed towards influencing a change in people’s thinking
2011
Western Union, Ndeke Road, Lusaka
I started from Jacaranda Mall, Ndola
My accomplishments included customer service, handling customer queries, carrying out
money transactions, handling petty cash and reconciliation
I also performed end of day writing of reports on the daily cash control
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
I compiled a weekly report at the end of the week showing the branch‟s financial situation for
the week
I further compiled a monthly report showing the financial activity for the month
Additionally, I did record-keeping and filing of documents that were used in my daily
operations
These successes show my propensity towards storing information and paying attention to detail
2007-2010
Sitas Boutique, 470 Shopping Mall, Cairo Road, Lusaka
I ran the boutique for three years, indicative of my ability to use initiative
August 2008
Consultant for Napsa/Esco Complex
I worked in conjunction with the Environmental Council of Zambia to draw up an
environmental impact assessment of the Napsa/Esco Complex
I shared in a stakeholders‟ briefing on the same, the stakeholders being the Lusaka City
Council, the Lusaka Fire Brigade, the Ministry of Tourism, among others
Consultant for Oddy’s Works
May 2006
I did an environmental impact assessment and helped compile detailed report for the same
September – October 2005
Project Concern International
Research Assistant
I carried out a community-based baseline study, involving extensive travel and visits to community
schools
The consultancy services I offered and the work I did at Project Concern evidence my ability to
carry out research and organise useful information
January – June 2000
Ronsmoen Trading (now defunct)
Receptionist/Sales Assistant
I handled phone calls and visitors
I arranged meetings and performed marketing work for the firm
The work I did here shows that I have people skills
RESEARCH
July – August 2004
Germany Technical Assistance to Zambia (GTZ)
I took part in the decentralisation program of local government carried out with the help of
GTZ. The research involved conducting a baseline study of local organisations in the
district of Sinazongwe with a view to making the Sinazongwe District Council a selfsustaining organisation
The other aim of the study was to identify the capacity needs of the community with a view
to future capacity building
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
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I gathered data and wrote a report on the findings of the baseline study
CONFERENCES/WORKSHOP S
I was usher at the International Conference on Health Reforms organised by the Central
Board of Health and World Health Organisation, among others
COMPETENCIES
I am able to coordinate with a team and work under minimum supervision
I am computer literate
I am able to carry out research (such as baseline studies) and compile reports
I have excellent interpersonal skills
I am skilled in public relations such as image building, media communications work, and
advertising and marketing work
I am able to do gender analysis and planning as well as economic policy analysis
I am knowledgeable in project planning, implementation, and analysis
I worked as a research assistant in relation to office love affairs and the effects of such on
the performance of industries, evidence of my social awareness
Reading, music and poetry, research, home-making
INTERESTS
LANGUAGES
English, Silozi, Chinyanja
REFERENCES
Mr John Simumba, Director, Tropical Environmental Management Experts, Findeco
House, 18th Floor, Room 19.Email:Tropicalenvironmental123@yahoo.com, Phone: 0977864057
Mrs Annie Mumbi, Country Director, American International Health Alliance (AIHA, a
ZAMCOM partner). Email: Amumbi@aiha.co.zm. Phone: 096 6 784790
The Dean, School of Humanities & Social Sciences, University of Zambia, Box 32379,
Lusaka, Zambia. Tel: 021 1 291381
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ROSINVEST -EIS
JOHN SIMUMBA
Cell: +260-0977 864057
E-mail: izukanji123@yahoo.com
Born:
21/09/1969
Sex:
Male
Marital Status:
Married
Nationality: Zambian
NRC No.:
276200/61/1
Professional Career: Environmental Consultant and Project Manager through training and
experience.
Professional Qualification: 1Metallurgical Engineer
University: University of Zambia School of Mines, Department of Metallurgy
Year: 1991-1996
Professional Qualification 2: Environmental Science
College: Metropolitan Johannesburg
Year: 2003-2005
Work Experience:
1997: Cobalt Plant in ZCCM-Nkana Division
1999: Alamo foundry-American company dealing in ferrous and nonferrous materials
2004: Found own company; Tropical Environmental Management experts.
Languages
1.
2.
3.
4.
5.
English
Namwanga
Bemba
Lamba
Lala
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
6. Mambwe
7. Lungu
Work Experience.
Coordinator and Director of Environmental Impact Assessments and Environmental
Project Briefs of the following Companies.
1.
NAME OF COMPANY
ENVIRONMENTAL JOBS
HYBRID (Z) Ltd
Environmental
assessment
OTHER JOBS
for
the
Establishment of Hatcheries throughout the
Country.
2.
Environmental Impact Assessment for the
MEDI-CARE (Z) Ltd
Construction of the Hospital in Lusaka
3.
LAMASAT
AND
LAMISE Environmental Impact Assessment for the
Construction of a Factory dealing in PVC
INVESTMENTS
Pipes, Plastic Tanks and Polythene bags in
Lusaka
4.
Environmental Impact Assessment for the
CHEVRON (Z) Ltd
Expansion of the Fuel Depot to accommodate a
new 2 million Liter Fuel Tank - Lusaka
5.
Assessment,
MEDICAL STORES
destruction,
sorting,
treatment
and
transportation of the treated
Pharmaceutical products to
the dumpsite.
6.
INTERNATIONAL
Assessment,
DRUG
destruction,
COMPANY
sorting,
treatment
and
transportation of the treated
pharmaceutical products to
the dumpsite.
7.
NGASA
Assessment and destruction
PHARMACEUTICALS
of 22000 packets of expired
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ROSINVEST -EIS
pharmaceutical Latex Gloves-
LIMITED
100pairs/packet
8.
PHARMACEUTICAL
Assessment,
REGULATORY BOARD
destruction,
sorting,
treatment
and
transportation of the treated
pharmaceutical products to
the
dumpsite
and
the
incinerator.
9.
WATCHTOWER
TRACT
BIBLE
SOCIETY
Assessment and disposition
&
of
OF
210 litres
of
Hypsin
Hydraulic oil, 80 litres of
ZAMBIA
Heat treatment oil and 440
litres of Trash liquids from a
mixture paints and thinners
10.
Assessment,
AUCHIM ZAMBIA LIMITED
sorting,
destruction,
treatment
and
transportation of the treated
pharmaceutical products to
the
dumpsite.
tonne
About
of
1.5
expired
pharmaceutical Products were
destroyed.
11.
SAFINA
Assessment,
PHARMACCEUTICALS
destruction,
sorting,
treatment
and
transportation of the treated
pharmaceutical products to
the dumpsite.
12.
B.O.C GASES
Assessment of the existing environment and Construction of a new Steel
preparation of an Environmental Project Brief.
Shelter or Filling Doc for
extra gas cylinders at the
Lusaka
Plant
for
BOC
GASES (formerly ZAMOX).
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
13.
MEBMARK TRANSPORT
ROSINVEST -EIS
Assessment of the existing environment and Construction of fuel tank
preparation of an Environmental Project Brief.
stand and bund wall,
Installation of fuel tank,
Construction of a 4 bed
roomed house ,servants
quarter, wall fence and
installation of sewer system
in Makeni
14.
BARLOWORLD PLASCON
The Designing of the Environmental
LTD
Monitoring Plan and carrying out its
implementation according to ISO 14001. The
project ran from 2005 to 2007.
15.
BARLOWORLD
The Designing of the Environmental
EQUIPMENT
Monitoring Plan and carrying out its
Implementation according to ISO 14001. The
project ran from 2006 to 2008.
16.
KWAKUWAHI LODGE-
Environmental Project Brief
MWINILUNGA
17.
SOLWEZI HOTEL-SOLWEZI
Environmental Project Brief
18.
REEDBUCK LODGE-
Environmental Project Brief
KABULONGA
19.
PAPER TREE LODGE-
Environmental Project Brief
SIAVONGA
20.
FALLS WAY LODGE –
Environmental Project Brief
LIVINGSTONE
21.
KOBIL SERVICE STATION-
Environmental Project Brief
KITWE
22.
CHAIMAN
Environmental Project Brief
MANUFACTURING
(MANGANESE MINE
KABWE)
23.
RAILWAY SYSTEMS –
Environmental Project Brief
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
KABWE
24.
RAINBOW TRADING-
Environmental Project Brief
LUSAKA
25.
ASHIA HAULAGE-LUSAKA
Environmental Project Brief
26.
CHISTEEL ZAMBIA-
Environmental Project Brief
LUSAKA
27.
ROCKWOOD QUARRY-
Environmental Project Brief
LUSAKA
28.
CHAT 3 BREWERY-LUSAKA
Environmental Project Brief
29.
CHIMELA BREWERY-
Environmental Project Brief
LUSAKA
30.
KHOLOWA SERVICE
Environmental Project Brief
STATION PETAUKE
31.
32.
CALIFORNIAN
Environmental Project Brief
BEVERAGES-LUSAKA
Production of plastic bottles
NAC 2000-LUSAKA
Environmental Project Brief
AIRPORT
33.
LAMASAT COMPANY-
Environmental Project Brief
LUSAKA
34.
LAMISE –LUSAKA
Environmental Project Brief
35.
FORM CAP –LUSAKA
Environmental Project Brief
Production of plastic bottles
36.
37.
MWANANSHIKU AND
Environmental Project Brief
COMPANY
Manganese Mining
SIWAYA LODGE
Environmental Project Brief
Building of Lodge
38.
JODAM MINING
Environmental Project Brief
Manganese mining
39.
MATCH CO. (Z) LTD
Environmental Project Brief
Eucalyptus Plantation
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
40.
ROSINVEST -EIS
Environmental Project Brief
BIWORLD (Z) LTD
Installation of a Diesel Tank
41.
Environmental Project Brief
PREMIER HOTEL
Renovation of existing building
42.
KEREN MOTORS (Z) LTD
Environmental Project Brief
Installation of a Diesel Tank
43.
KRONOS HOSPITAL
Environmental Project Brief
Construction of a private Hospital
44.
HAUCHANG RED BRICK
Environmental Project Brief
production of red bricks
45.
KINGFISHER MILLING
Environmental Project Brief
Mealie Meal production
46.
LIMBE PROPERTIES
Environmental Project Brief
Construction of a storey building
47.
DOLOMITE AGGREGATE
Full- Environmental Impact Assessment of the
effects of Lime Production on the surrounding
Environment in Lusaka West
48.
49.
FLY
DRAGON
(CHAMA Full Environmental Impact Assessment of
DISTRICT)
wood harvesting and Saw Milling
NASLA CEMENT
Full-Environmental Impact Assessment for the
construction of the cement plant in Lusaka
with the Capacity of 1500 tonnes per annum
50.
51.
LEVY PARK – FORMER
Full Environmental Impact Assessment
ESCO.
Construction of multiuse building.
ODY’S HOTEL
Full-Environmental Impact Assessment on the Construction of a pump
construction of Premier Hotel with 200 bed house, Installation of sewer
capacity in Lusaka.
line stretching about 2.8km,
Plastering of hotel rooms and
painting lots and Construction
of oil (fuel) separators for
Oddy‟s service stations.
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52.
ROSINVEST -EIS
ARAB Full-Environmental Impact Assessment on the
FLAME
construction of the five Star hotels with 200
CONTRACTORS
bed capacity in Lusaka.
53.
(LIBUYU Full-Environmental Impact Assessment for
SWASCO
SANITATION
PROJECT construction of sewer line and bio digesters.
LIVINGSTONE)
54.
DONCROFT INVESTMENTS Full-Environmental Impact Assessment for
provision of residential serviced plots.
(CHELSTONE)
55.
56.
FLY
DRAGON
(SIKONGO Full-Environmental Impact Assessment for
SIAVONGA)
Timber harvesting.
FLY DRAGON (LUANGWA)
Full-Environmental Impact Assessment for
Timber harvesting.
57.
58.
BANTU
PARK
SALES Environmental Project Brief
CENTER-LILAYI
Sales Center
WAMUKUPIKA
Environmental Project Brief
Lodge-Emmasdale
59.
MICMAR INVESTMENTS
Environmental Project Brief
Office block-Along Great East Road
60.
OFIA INVESTMENTS
Environmental Project Brief
Mineral Exploration-Solwezi
61.
KALABA
Environmental Project Brief
Mine-Kitwe
62.
DOLPHIN
Environmental Project Brief
Lodge-Emmasdale.
Technical Corporation and Professional Support
Tropical Environmental Management Experts is registered with the Zambia Environmental
Management Agency (ZEMA)-the Statutory mandated body responsible for regulating
Environmental Management., Local Authorities and other professional bodies in the country.
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also has Technical Corporation with SAVA –
Tropical Environmental Management Experts
Sonderabfallverbrenunganlage of Germany and enjoys professional support from Sustainable
Environmental Management Institute (SEMI) of Germany.
It also includes Dr. Heino Vest - International Consultant on Waste Management and formerly
Director GTZ sub-Saharan Africa.
Prof. Simukanga – Metallurgist and Vice Chancellor, University of Zambia and Dr. Edward
Lusambo – Head of Department, Dept. of Agricultural Engineering, Sch. of Engineering, UNZA.
Computer Knowledge
Proficient in;
Microsoft Office.
E-MAIL:tropicaenvironmental123@yahoo.com
REF:
1. Vice Chancellor Professor Simukanga
2. Professor Jere
3. Professor Whitker
4. Professor Nkonde
SIGNATURE
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FELIX CHABALA
Curriculum Vitae
NAME:
Felix Chabala
PROFESSION:
Civil /Environmental Engineer
DATE OF BIRTH:
7th July 1969
SEX:
Male
NATIONALITY:
Zambian by birth
LANGUAGES:
English (Fluent)
MOBILE NO:
+260 955 880216
+260 966 880216
E-MAIL
felixchabala@yahoo.com
Affiliations:
Member of the International Association of Impact Assessment (IAIA)
Engineering Institution of Zambia (EIZ)
Key Qualifications
Felix Chabala holds a Master‟s Degree in Water Engineering from the University
of Perugia in Italy as well as a Bachelor‟s Degree in Civil Engineering from the
University of Zambia. He has over 15 years‟ experience in the construction
industry and environmental management, compliance monitoring and enforcement
in Zambia. He has supervised various infrastructure developments like Roads,
Bridges and Water related projects.
Relevant working experience from present and previous assignments includes:
2001 –Jan 2010 Working as Principal Inspector - Environmental Impact
Assessment (EIA) at the Environmental Council of Zambia (ECZ). He was in
charge of the implementation of a component on Environmental Management and
Compliance Monitoring of various mining related projects under the Nordic
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Development Fund/World Bank Funded Copperbelt Environment Project (CEP).
In addition, Felix spearheaded the review, carried out verification inspections and
made recommendations for decision making of over 100 Environmental and Social
Managements Plans as well over 1000 environmental Project Briefs many of them
donor funded. He has also carried out compliance inspections and environmental
audits on all companies that submitted ESMPs to the ECZ.
EDUCATION AND PROFESSIONAL QUALIFICATIONS
Year
2007
Qualifications
Master of Engineering – (Water)
Institution
University of Perugia - Italy
1994:
Bachelor of Engineering Degree
in Civil Engineering (B.Eng.)
School of Engineering,
University of Zambia
1989:
„O‟ Level, School Certificate
Lusaka, Zambia
David Kaunda Sec Tech Sch.
PROFESSIONAL COURSES ATTENDED
Environmental Monitoring
December 2007
Strategic Environmental Assessment (SEA), South Africa
August 2006
Risk Management in Development Planning at Charmers University
Gothenburg, Sweden
April – May 2002
Advanced Certificate in Environmental Impact Assessment (EIA),
Sweden Stockholm
June – July 2003
Environmental Auditing and Communication
November 2002
DETAILED DESCRIPTION OF PROFESSIONAL EXPERIENCE
2011 to date
The following table indicates some EIA studies projects undertaken:
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Name of Project
Client
Environmental Impact Statement for Mopani
Copper
Mopani Copper Mines Area D extension Mines Plc
open Pit in Kitwe
Shimzu Corporation Quarry in Lusaka
Shimzu
Corporation
Huate International Construction Asphalt Huate International
Plant in Lusaka
Environmental Impact Assessment for an Universal Mining
Iron Ore Project in Nampundwe
and
Chemicals
Industries Limited
Resettlement Action Plan for Twashuka NFC
Africa
and Mukulumpe Communities
Mining Plc
Preparation of a Chapter on Land for the Zambia
Zambia Environment Outlook Report
Environmental
Management
Agency
Evaluation of innovative environmental Civil
Society
project proposals for possible funding
Environment Fund
Auditing of Environmental and Social Albidon Zambia
Management Plan
Limited
ROSINVEST -EIS
Year
2013
2013
2013
2012
2011
2011
2011
2011
2001 –Jan 2010 Environmental Council of Zambia (ECZ) LUSAKA–
Position: Principal Inspector -Environmental Impact Assessment
(EIA)
Achievements
As head of the Environmental Impact Assessment (EIA) Unit, I
was responsible for reviewing all EIA submitted for approval,
arranged for public hearings, conducted disclosure meetings and
made recommendations for board approval.
Participating in the planning, training, organizing and review of
the DANIDA Strategic Environmental Assessment (SEA) for the
Phase II of the Mongu – Senaga Road Project.
Coordinated the preparation of the draft 2006 Zambia
Environmental Outlook chapter on Mineral Resources
Reviewed the Environment Programmes and Natural Resources
Component of the Fifth National Development Plan (FNDP)
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Did peer review of the Repackaging of Environment and Natural
Resources Programmes of the Fifth National Development Plan
DRAFT Natural Resources Concept Note
Coordinates the various Government Departments/Ministries that
are stakeholders in the Environmental Impact Assessment
Process.
Carried out public disclosure of all donor/GRZ funded projects
that are subjected to Environmental Assessment
Coordinates the activities of Environmental Management
Component of the NORDIC/World bank funded Copperbelt
Environment Project.
Carried out statutory environmental Audits on the following
Approved Environmental and Social Management Plans
(ESMPs) in order to meet the output indicators for the CEP:
- First Quantum Mining and Operations Limited –
Bwana Mkubwa Mine Site
- Konkola Copper Mines Plc – Nampundwe Mine
- Konkola Copper Mines -Nkana Smelter
- Konkola Copper Mines Plc – Nchanga Mine Site
- Kansanshi Mine
- Chambishi Smelter
- Over 30 Tailings dams owned by ZCCM –IH Plc
Provided legal guidance, carried out reviews, inspections
and recommendations of the following Environmental and
Social Management Plans for the following facilities:
- Konkola Copper Mines Plc (KCM)Heap Leach project in
Chingola Zambia,
- Mopani Copper Mines Plc underground in-situ leaching
project in Mufulira,
- Mopani Copper Mines Plc underground in-situ leaching
project in Mufulira
- KCM Plc – Chingola Heap Leach Project
- KCM Plc Fitwaola Open Pit
- Mopani Copper Mines Plc in Mufulira and Kitwe
- Bwana Mkubwa Mine in Ndola
- Chambeshi Metals Plc in Chambeshi
- Kansanshi Mine Plc in Solwezi
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-
ROSINVEST -EIS
KCM Plc Nkana Smelter
KCM Plc Nchanga Smelter
KCM Plc Nampundwe Mine
KCM Plc Nchanga Mine
KCM Plc Konkola Mine
Supervised the implementation of the following
Resettlement Action Plans: KCM Kawama Project funded
by World bank and, Zambia Electricity Supply
Rehabilitation project funded by world bank
Supervised the following public disclosure meetings for the
following mine projects ZCCM – IH Counterpart
Environmental Management Plans for Bwana Mkubwa,
Luanshya, Chibuluma, Nchanga, Nkana, Chililabombwe,
Mufulira and Several abandoned Tailings Dams and Mine
Dumps in all Towns on the Copperbelt province of Zambia.
Carried out environmental Compliance monitoring on over
200 facilities over a period of 8 years
Carried out environmental Licensing (Waste Generation, air
Pollution, Pesticides and Toxic Substances) on over 500
facilities in Zambia
Carried out review and made recommendations on over
1000 Environmental Assessment Reports over a period of
eight years.
Carried out the review of Environmental Impact Assessment
for the Mulungushi Dam in Kabwe for National College of
Management
Carried training in Environmental Management for the
following Companies: Chilanga Cement Plc, KCM Plc, all
local Authorities in Zambia, Zambia National Tourism
Board
Carried out national wide training of all local authorities in
Zambia under the support from the World Bank in 2002 2003
1997 - 2001 RANKIN ENGINEERING CONSULTANTS
KASAMA, ZAMBIA
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POSITION: SECTION ENGINEER (Infrastructure)
Draft tender documents, invite bid and made recommendations to national
Roads board on various small scale road works in Northern Province.
Supervised the construction of the Vitondo dam in Isoka funded by the
Economic Expansion in Outlying Areas (EEOA)
Designed the small earth dam and weir. The design involved material specs. i.e.
grade of concrete for the weir., materials for dam walls , angle of dam walls.
Designed 3 culvert bridges and supervised their construction.
Designed earth roads ( Over 1000 km) in the following districts of Zambia:
- Chinsali
- Nakonde
- Mpika
- Isoka
This involved design for drainage, small bridges, material specs, and levels.
Carried out road surveys in terms type and density of potholes, drainage, road
Deformation, type and width of cracks.
Prepared tender documents and did tender adjudication for labour based Road
contractors
1995- 1997
ZCCM, KONKOLA DIVISION - CHILILABOBWE
Position Held: Section Engineer- Civil, Mechanical Construction and Contract
Management
Achievements:
Carried out contract administration for the Mine involving, Invitation to Tender,
Tender Evaluation, made recommendation for Award of Contract and draft
Contracts for successful bidders
Carried out the routine maintenance of the Lubengele Tailings dam, pipeline,
surface water management structures in Chililabombwe for KCM/ZCCM
Constructed the Lubengele embankment across the Lubengele River in
Chililabombwe
Constructed an emergency earth embankment to link Kawama Township with
the rest of Chililabombwe when the Lubengele Tailings dam flooded.
Carried out road surveys (density of pot holes, drainage, types of cracks and
size etc.) to determine amount of repairs required.
Carried out Road resurfacing (8.0Km) in the townships using bitumen.
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Carries out Maintenance of roads (60 Km tarred and 100Km gravel) and
buildings in the townships (over 5000 structures).
REFEREES
1)
Mr Patson Zulu
Manager – Inspectorate
Environmental Council of Zambia
P.O Box 35131
LUSAKA
Mobile Number: 260 955 833581/0977 470849
Office: +260 211 254094
E-mail: pzulu@necz.org.zm
2)
Mr Yoram Simbeye
Bicon Zambia Limited
4 Omelo Mumba Road
P.O Box 39528
Lusaka
Zambia
Cell 0977 - 873970
Office: 0211 232978
3.
James Tembo
Senior Lecture – Department of Civil and Environmental Engineering
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
Great East Road Campus
P.O Box 32379
LUSAKA
Zambia
Office: 0211 290962
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P.O BOX 34933, LUSAKA, ZAMBIA.
PHONE +260 979 301544 • E-MAIL CHIBS23@HOTMAIL.COM
NCHIMUNYA HIMUNYANGA
PERSONAL INFORMATION
Age – 23 years
Sex - Female
Nationality - Zambian
NRC # - 880388/11/1
OBJECTIVE
To create an accurate presentation of myself for the application for
employment.
EDUCATION
[ 1990 - 1996 ]
Attended grades one to seven at the named school.
Lumuno Primary School
[ 1997 – 2001 ]
School
Attended grades eight to twelve at the named school
Obtained GCE O’level Certificate.
St Mary’s Secondary
[ 2003 – 2004 ]
Zambia
Attended first and second year in the School of Natural Sciences.
[ 2005 to date ]
University
Attended first, second, third and fourth and final years of study
Completed a Bachelor of Science degree in Forestry.
[ City, State ]
University of
The Copperbelt
WORK EXPERIENCE
[ 15th January 2007 – 28 February 2007 ]
Copperbelt Forestry Company
Intern at the Copperbelt Forestry Company’s Kalibu plant in Kitwe.
Carried out quantity and quality analysis, for the purpose of quality
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control, on several company products.
Compiled a report written to highlight some of the shortcomings of the
various departments at the company.
Compiled a final report establishing standard consumptions and quality
control system in various sections.
[ 15th September 2008 – 28 September 2008 ] Martin Sampa & Associates
Enumerator for Environmental Baseline Study.
Compiled a legal and policy framework for mineral exploration.
Carried out data collection required for the compilation of an
Environmental Project Brief, in concerned areas.
[ 29th August 2008 – January 2009 ] New Kaloko Pilot Project in Urban
Agriculture.
Enumerator for Pilot Project Impact Assessment.
Carrying out monthly assessments in the project area on the themes of
gender, socio-economic and the community environment.
Conducting focus group discussions to be used in gender, economic,
environment, and health and nutrition scheme.
EXTRACURRICULAR ACTIVITIES
Vice President of the Copperbelt University Natural Resources and
Environmental Society (CUNARES) 2006-2007.
Trustee of the Copperbelt University Natural
Environmental Society (CUNARES) 2007-2008.
Resources
and
The society is a group of students from the School of Natural Resources at
the Copperbelt University, a leading force in the coordination and unity of
all its members in carrying out natural resource management projects and
advancing public awareness of the beneficial influence of our
environment.
HOBBIES
Reading various literatures and playing volleyball.
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REFERENCES
Mr. S. Mwewa
Operations Manager
Copperbelt Forestry Company
(+260 977 844508)
Mr. R. Kasubika
CUNARES Patron
The Copperbelt University
(+260 979 319871)
Mr. K. Mwelwa
Assistant Dean – School of Natural Resources
The Copperbelt University
(+260 966 909250)
Mr. Martin Sampa
Managing Associate
Martin Sampa & Associates-Environmental Advisory Services
P.O Box 90885,
Luanshya, Zambia.
(+260 977 437612)
Dr. J. Mwitwa
Project Coordinator
New Kaloko Pilot Project
(+260 977848462)
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ANNEX 5
MINING LICENSE
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ANNEX 6
DALED CERTIFICATE OF
INCORPORATION
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ANNEX 7
ROSINVEST CERTIFICATE
OF INCORPORATION
235
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ANNEX 8
MINE LAY OUT PLAN
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ANNEX 9
CONCENTRATOR DESIGN
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ANNEX 10
SMELTER DESIGN
242
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ANNEX 11
CRUSH PLANT
244
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ANNEX 12
TIN PROCESSING PLANT
246
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ANNEX 13
STONE PRODUCTION
LINE
248
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TROPICAL ENVIRONMENTAL MANAGEMENT EXPERTS
ANNEX 14
GRAVITY
CONCENTRATOR
CIRCUIT
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ANNEX 15
ROCK CRUSHING
CIRCUIT
251
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ANNEX 16
TANK DESIGN
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ANNEX 17
UNZA LABORATORY
RESULTS
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ANNEX 18
LETTER FROM THE
CHIEF
254
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ANNEX 19
SITE LOCATION MAP
255
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ANNEX 20
TOPOGRAPHICAL MAP
256
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ANNEX 21
GEOLOGICAL MAP
257