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1999-08-23_HYDROLOGY - M1999051
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1999-08-23_HYDROLOGY - M1999051
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Last modified
3/22/2021 5:08:43 AM
Creation date
10/24/2011 1:27:44 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999051
IBM Index Class Name
HYDROLOGY
Doc Date
8/23/1999
Doc Name
Surface & Ground Water Monitoring Plan
From
TRC Hydro-Geo Consultants
To
DRMS
Media Type
D
Archive
No
Tags
DRMS Re-OCR
Description:
Signifies Re-OCR Process Performed
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20 RISK ASSESSMENT /MANAGEMENT <br />► Hazard assessment <br />► Exposure assessment <br />► Consequence assessment <br />► Risk characterization <br />Each of these steps is discussed below. The <br />five point scale proposed for a qualitative risk <br />assessment consists of the following <br />descriptors: <br />► negligible <br />► very low <br />► low <br />► medium <br />► high <br />Before embarking on the four step approach, <br />it is necessary to identify potential failure <br />modes and mechanisms. These are identified <br />based on a knowledge of the site and the <br />proposed design elements, as well as experience <br />on past failures at mine sites. This step if <br />the risk assessment is very similar to design <br />engineering where each failure mode is <br />identified and a mitigative design developed. <br />Hazard Assessment <br />In the first step hazards associated with a <br />specific situation are identified; e.g., an <br />investigation is made of mine waste and tailings <br />to be deposited into an impoundment, or the <br />waters to be discharged from a treatment plant. <br />The constituents of concern are identified and <br />described as to the hazards they may pose to the <br />environment. <br />The final results of the hazard assessment is <br />the selection and description of those hazards <br />which are present for each potential failure <br />mode. <br />Exposure Assessment <br />The next step in the qualitative risk <br />assessment is to perform an exposure assessment. <br />For each potential failure mode a substance <br />which poses a hazard (such as sediment) can be <br />transported from its point of release to where <br />it impacts the environment. Transport can take <br />place through various media, such as over land, <br />through surface water, groundwater and air. <br />Exposure to the environmental systems can be <br />through physical means (e.g. sediment directly <br />covering land and vegetation or released into <br />streams) or chemical means such as heavy metals <br />released into streams. The elements of the <br />exposure assessment which must be considered <br />include failure mechanism, initiating events, <br />relative risk of release, magnitude of release, <br />duration of release, pathways and ecosystem at <br />risk. The final result of the qualitative <br />exposure assessment is the description of the <br />relative magnitude of exposure associated with <br />each potential failure mode using the five point <br />scale. <br />The hazard assessment and exposure assessment <br />steps address the questions: <br />► what can happen? <br />► how likely is it to happen? <br />Consequence Assessment <br />The third step is evaluating the consequences <br />or impacts of a hazard following release and <br />exposure of a local ecosystem, e.g. the <br />consequences to fish of the release of heavy <br />metals into a stream. Consequences are also <br />described using a five point scale. <br />The consequence assessment addresses the <br />question: <br />► if it does happen, what are the <br />consequences? <br />Risk Characterization <br />The fourth, and last step, is to characterize <br />the risk associated with each failure mode based <br />on the hazard assessment, exposure assessment <br />and consequence assessment. Risk is also <br />characterized using the five point scale. <br />Figure 1 presents a schematic of the proposed <br />qualitative environmental risk assessment <br />approach. <br />EXAMPLE APPLICATION OF QUALITATIVE <br />RISK ASSESSMENT <br />Introduction <br />In applying a qualitative risk assessment to <br />a specific mining project a number of <br />assumptions must be made, for example, a project <br />site can be divided on the basis of geographic <br />location and activity into different areas such <br />as: <br />► Mine - mine, mine waste disposal, water <br />management system. <br />► Mill and Tailings - mill, tailings <br />disposal, water reservoir. <br />► Transportation, Storage and Handling <br />Facilities - dock, roads, storage at mine <br />and mill. <br />Each of these areas can further be divided <br />into components such as the waste rock stockpile <br />in the mine area and the individual tailings <br />impoundments. Such division is useful in <br />identifying individual failure modes. <br />Failure modes can be identified for each <br />component during four phases of project <br />development. The four phases used in this <br />example are: <br />► Construction <br />► Operations <br />► Reclamation <br />► Closure <br />Project Description <br />Figure 2 shows the main components of the <br />example project. The project is located on a <br />coastal plain. The major environmental factors <br />associated with the project are described below. <br />Climate. Frequent frontal systems combine to <br />produce abundant precipitation throughout the <br />region, especially along west - facing mountain <br />slopes. Winters are mild, and snow on the lower <br />elevations is a minor component of the total <br />precipitation. Average precipitation increases <br />with increasing elevation from approximately <br />1700 to 2200 millimeters per year. Average <br />monthly temperatures range from about 1 °C in <br />January to approximately 14 °C in July and <br />August. <br />Phvsioaraphic Units. The mine area is located <br />along the boundary of two major physiographic <br />units. The lowlands to the east are generally <br />characterized by extensive areas of little to no <br />
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