HomeMy WebLinkAbout20190035 Ver 1_More Info Received_20190905F]J PIEDMONT
LIT H I LIM
September 5, 2019
Ms. Olivia Munzer
NC Wildlife Resources Commission
Rogers Depot, 1718 NC Hwy 56 West
Creedmoor, NC 27522
Subject: Piedmont Lithium Project (SAW -2018-01129)
Additional 10 Day Agency Comment Period
On behalf of Piedmont Lithium, Inc., HDR would like to thank you for your questions that arose
during the additional 10 day comment period that began on August 20, 2019, and ended on August
30, 2019. The NC Wildlife Resources Commission provided the eight questions below in an email
format.
1. Will they mine any of the pits simultaneously during the life of the mine?
Yes, it is anticipated that as many as two pits will be open at any given time. According to
the current mine plan the mine sequence will be east pit, south pit, central pit, then north pit.
Additionally, once its reserves are exhausted, the east pit will be backfilled with waste rock.
2. Table 2 refers to PW -1 groundwater baseline. I was unable to find its location on a figure.
PW -1 is the aquifer pump well and is located north of Hephzibah Church Road and north of
the East Pit.
LEGENDi'-#
IP Project Boundary
0
(963 ac.)
Pit Extents
Pumping Well
A Observation Well
Gaston Co. Receptor
~
Well
HDR Delineated
Streams
0 HDR Delineated Pond
HDR Delineated
0
Wetlands
Desktop Streams
® Desktop NWI Wetland
100 -Year FEMA
(�\
Floodplain
T� Culverts
t —h -1 600 f—t
-
N
t
-Mw-1
MW -5
�9
WON.
0 Feet 1.800 _ 'ir' f
MW -4
- O
s •
i
Figure 1. Location of Pumping Well, Observation Wells, and Receptor Wells.
OW -21) W-25
PW -1 \
OW -1D OW -15
41
F]J PIEDMONT
LITHIUM
3. It appears that the stream flow was only measured in May. Can they explain as to why it
wasn't measured during other times of the year (high and low flow)?
We noted that there was only one measurement and that it was not during low flow. All
available data was provided to support the model, which presents the greatest amount of
drawdown or withdrawal at the full excavation limit of each mine pit, in effect, the worst-case
scenario as noted in Question 5, below. Given timing, project schedule, and project budget it
was measured at the time noted.
4. What is the distance from the outflow (energy dissipater) to the streams?
Please see the attached table with the requested information. Figure 1 in Appendix C in the
Public Notice Response (dated May 31, 2019, revised July 3, 2019) is also attached,
depicting the proposed outflow locations.
5. How long will the pits be in operation? The dewatering model assumes a steady state
withdrawal, therefore a reduction in baseflow, for the entire timeframe that each pit is being
mined. I'm assuming that will be years, but is it 5 years, 10 years, more?
The anticipated total life of mine under the proposed plan is 11 years; but that may be
adjusted, including increased, based on the actual declaration of reserves.
We also note that the hydrogeological model presents the greatest amount of drawdown or
withdrawal at the full excavation limit of each mine pit. This is in effect the worst-case
scenario with respect to drawdown. Dewatering therefore should be less than the figure
presented until the pit excavation approaches its ultimate pit shell.
Additionally, once each pit is exhausted and mining operations or waste backfill operations
have concluded, dewatering will cease in that pit. Pits will be allowed to flood at the
conclusion of operations.
6. They say the dewatered pit water will be applied to streams or wetlands within the project
boundary. So, I would assume the net outflow from the site may actually be higher than
normal while the pits are active. Can they confirm this?
It is possible that the net total outflow from the site will be greater than normal in the
presence of dewatering operations.
7. I'm not clear on how they are defining baseflow, which is what they are using as the
denominator for comparisons. Are they assuming baseflow is a static number or if it
changes seasonally? My understanding is the latter. If I'm correct, then the percentage
impact will vary through the year. So, does their characterization of (up to) a 10% reduction
in baseflow represent a full and complete understanding of the impacts?
Base flow is the groundwater that discharges to the stream and should not vary seasonally
throughout the year, but base flow could be affected by long term climate events, such as
droughts. Variability in stream flow is usually from runoff and evapotranspiration, while base
flow remains constant. Since base flow only is the lowest flow condition, the model
estimates the greatest amount of impact (estimated worst case scenario) that should be
seen. Here is an explanation of base flow from the USGS: https://www.usgs.gov/special-
topic/water-science-school/science/base-flow-rivers?gt-science center objects=0#gt-
science center objects
P I E DMON T
LITHIYM
8. There are limited data points. They state they are willing to do additional data collection and
model refinement. Is that something they can do and in what timeframe?
Having worked extensively on the model presented, we respectfully believe that the data
presented is adequate and a good representation of potential effects the proposed activities
may have on groundwater.
In fact, the model assumes the worst-case scenario with respect to drawdown and it does
not take into account the continuous input of water from offsite. It is likely that potential
effects may be less than modeled.
Additional data collection, specifically pump tests, and modeling are not likely to result in a
model with greater accuracy, or present results which are likely to show greater impacts than
those currently presented.
Piedmont has collected groundwater and surface water quality data for a number of months,
which was submitted (data up to that point) with the Public Notice response on July 3, 2019
(dated May 31, 2019, revised July 3, 2019). This data collection has continued and will
continue through the end of the year.
On behalf of Piedmont Lithium, Inc., HDR is submitting this response to the eight questions that
arose during the additional 10 day, agency comment period. Should you have any questions or
require additional information following your review of the enclosed materials, please contact me at
(704) 338-6710 or kelly.thames(@hdrinc.com.
Sincerely,
HDR, Inc.
Pell�_,�ames, PWS
Environmental Project Manager
Attachments: Tabulated Outflow Distances to Streams
Piedmont Lithium Site Plan Map
cc: Patrick Brindle, Piedmont Lithium, Inc.
ARSHUL ILLE
[sem 11
ENERGY DISSIPATOR TO STREAM - FLOW DISTANCE
PROJECT PIEDMONT LITHIUM
BY CFH
DATE 9/5/19
SHEET 1OF1
PROJECT NO. PLIT101
CHECKED BY JAA
DATE CHECKED 9/5/19
Pond
Flow Distance to Jurisdictional Stream
(ft.)
EWR SEDIMENT POND 1
414.92
EWR SEDIMENT POND 2
56.95
EWR SEDIMENT POND 3
1209.55
WWR SEDIMENT POND 1
229.72
WWR SEDIMENT POND 2
778.48
WWR SEDIMENT POND 3
37.78
WWR SEDIMENT POND 4
149.32
WWR SEDIMENT POND 5
44.86
SEDIMENT POND SB1
18.54
SEDIMENT POND SB2
38.83
SEDIMENT POND SB3
10.95
SEDIMENT POND SB5
95.14
PIT DISCHARGE POND N
92.44
PIT DISCHARGE POND CN
226.84
PIT DISCHARGE POND CS
184.99
PIT DISCHARGE POND S
427.79
PIT DISCHARGE POND E
324.82
MAINTENANCE AREA
FUEL YARD
BAH
HZICHURCH RD ��
-;PTO THRU TRAFFIC
�OIICAL USE ONLY O
HEPHZIBAH CH RCH RDI-
,., CLOSED ;� aE c No. 2
Gp@"CPNWEBBEC"u"
G
NOTES:
1. Sequence of pit clearing to include stripping of East Pit,
South Pit, Central Pit, and North Pit. Sediment/Erosion
G
ontrol for pit clearing stages to involve placement of
SU
silt fence (steel piles) in downslope areas of pits.
2. Disturbed ground during bridge Construction, through the
use of Best Management Practices (BMP) (e.g. sediment
fences, erosion control structures diversion ditches, silt
fence and revegetation measures), runoffwill be
J intercepted before it �- is able to reach the creek. Sediment
yield from disturbs areas will be managed by sediment
Control structures and temporary and permanent
vegetal on, such that any added sediment load to the
Creceiving stream is expected to be minimal during
construction activities. Drainage control structures, along
with the Contemporaneous regrading and revegetation of
disturbed areas are expected to prevent or minimize the
�contributions of suspended solids. All disturbed areas will
�-'-� be seeded as quickly as possible. Once the bridge
construction is completed, disturbed areas will be
reclaimed to further minimize runoff.
E- SCREENING NcBE�oNO S��,��/!/
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.a .o
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z E MTSG�s aEXCAVATIO LGwwATER asING - I i
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,.- ... ENCE m O �t
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i t six, I
— gaNRT ° II ,`UNITS°FE �A�ATG
a'AN� --II 6 FEET HIGH
i ru t
H111 Ik
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PROPOSED
SEE NOT '✓ �� ,y
23 OB -3
i
MINE PT CONSTRUCTION SEQUENCE
SEE NOTES .!� �
Q
LEGEND
\/
11 /,
ti y"
100 YR. FLOOD PLAIN
� DELINEATED WETLANDS
DELINEATED PONDS
DELINEATED STREAMS
' ` _ -==I- PROPOSED DITCHES
_- PROPOSEDFLUMES
.. .. .o BUILDING/STRUCTURE
EWR DISPOSAL AREA
WWR DISPOSAL AREA
_ - EXTENTS OF MINE PITS
AND EXCAVATION
ASTINGS RD. HAULROAD CULVERTS
.., �,. CLOSED HAULROAD SUMPS
RECEPTOR WELLS
; ROADCLOSURE
a� SUPER SILT FENCE
O � OBSERVATION WELL
DO PIEDMONT PROPERTY LINE
\ / MINE PERMIT LINE
25 FT MINE PERMIT BUFFER
FT LOT BUFFER
200 FT STRUCTURES BUFFER
RESIDENTIAL BUFFER
SITE / MINE MAP
PLAN VIEW
,... _ HEPHZIBAH C URCH RD.
CONTOUR rNrEBVAL=zFEET
CLOSED ,...._._ o M 60 No
—41 1- SCALE 1"•100'
Dv[e Revision
DESIGNED: JDP, COS
PIEDMONT LITHIUM, INC. DRAWN : dDP, cos
SHEET PIEDMONT LITHIUM CHEKEDi 24/ P I E DIy1Q N T
LINCOLNTON WEST QUADRANGLE DATE: AS SHOWN
19
OF 1 SCALE - AS HOWN
GASTON COUNTY, NORTH CAROLINA PROJECT NO.: PLIT101 LITHIUM
FILE ND.. —11 -Bluefield, VA May, 2019 JP SM CS JA