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notebook - Southwest Florida Water Management District

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Background<br />

Depending on the characteristics of the site where phosphate matrix is to be mined, the mining process<br />

will usually require some form of dewatering of the SAS. Typically, pre-mining dewatering activities are<br />

conducted to ensure ground stability and to ensure mine cuts are sufficiently free of water to allow the<br />

mining equipment to operate safely and efficiently. Effective dewatering of the mining area also enables<br />

the operator to visually evaluate the depth and extent of the mineral reserve and maximize resource<br />

recovery. Dewatering activities have the potential to result in drawdown of the SAS. The extent of the<br />

drawdown is dependent on a number of factors including the overall depth of mining, the overburden<br />

thickness, the duration of the dewatered open cut, and the hydrogeologic characteristics of the<br />

overburden soils, including but not limited to, the absence or presence of aquicludes and/or aquitards and<br />

the vertical and horizontal hydraulic conductivity of the overburden soils.<br />

For this reason, an approach has been developed to define a Mandatory Mitigation Distance (MMD)<br />

(formerly referred to as the “setback” distance) for each mine site. The MMD will be used to determine<br />

when the implementation of a Site-Specific Drawdown Mitigation Plan (SSDMP) is required. Dewatering<br />

activities outside of the MMD are presumed not to cause impacts.<br />

Since Mine Activities encompass a broad range of hydrogeologic and other site specific characteristics,<br />

the MMD must be, to a certain extent, site specific. Determination of the MMD must also be conservative<br />

to ensure that it represents the full potential extent of SAS drawdown that could occur in the absence of<br />

mitigation measures.<br />

Methodology for Establishment<br />

Mosaic uses site specific field data and a detailed engineering analysis of the potential, unmitigated SAS<br />

drawdown at a site. A transient flow seepage analysis will be accomplished through the use of the<br />

computer application SEEP/W, developed by GEO-SLOPE International LTD, or other mutually agreed<br />

upon method to determine the maximum extent of dewatering drawdown influence in the SAS.<br />

The Permittee shall use a 0.5-foot and greater cumulative drawdown in the SAS from the groundwater<br />

model and dewatering modeling as a guide for determining when the MMD process contained within the<br />

EMP is to be implemented. Numerical modeling is preferred over analytical models for determining the<br />

estimated range of drawdowns to occur from mining and dewatering. However, as updated models and<br />

other techniques are made available, these shall be taken into consideration for use.<br />

A stratigraphic cross section will be developed adjacent to environmental features/property boundaries for<br />

determining the depth of overburden and matrix, and to develop stratigraphic profiles from land surface<br />

down to the bottom of the mineable matrix. Prospecting data is suitable for use in determining depth of<br />

overburden and matrix. Split spoon, continuous coring, or another generally accepted geotechnical<br />

investigation technique shall be the preferred methods for developing the stratigraphic profile from land<br />

surface to the top of the matrix.<br />

Once the stratigraphic profile of the surficial aquifer has been determined, field derived hydraulic<br />

conductivity measurements will be input in the seepage model for the differing SAS stratigraphic units and<br />

cast overburden (if present) in the model. The determination of the MMDs for each mine area will be<br />

based on the results of the approved modeling technique as set forth below or such other appropriate<br />

MosaicFertilizer,LLC–WUP20011400.025–Environmental<strong>Management</strong>Plan<br />

Page7<br />

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