Smcra Noi Final

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    NOTICE OF VIOLATION AND INTENTION TO SUE

    PURSUANT TO 30 U.S.C. 1270(a)(1)

    To: Ken Salazar, Secretary of the Interior

    United States Department of the Interior

    1849 C Street, N.W.Washington, D.C. 20240

    Joseph Pizarchik, Director

    Office of Surface Mining Reclamation

    and Enforcement

    1951 Constitution Ave. N. W.

    Washington, D. C. 20240

    Allen D. Klein, Regional Director

    Western Regional Office

    Office of Surface Mining Reclamationand Enforcement

    P.O. Box 46667

    1999 Broadway, Suite 3320

    Denver, CO 80201-6667

    Bill Brancard, Director

    Mining and Minerals Division

    Energy, Minerals and Natural ResourcesDepartment

    1220 South St. Francis Drive

    Santa Fe, NM 87501

    San Juan Coal Company

    P. O. Box 561

    Waterflow, NM 87421

    In accordance with 30 U.S.C. 1270(b) and 30 C.F.R. 700.13, Sierra Club notifies each

    of you that, on or after the 60th day from the date of this notice, it intends to initiate a citizen suit

    against San Juan Coal Company (SJCC) pursuant to Section 520 of the Surface Mining Control

    and Reclamation Act of 1977 (SMCRA), 30 U.S.C. 1270. Sierra Club intends to base the suit

    on SJCCs continuing violation of SMCRA and of rules and regulations issued pursuant to SMCRA

    that comprise the approved state regulatory program for New Mexico (the New Mexico program),

    30 C.F.R. Part 931.

    I. THE PROVISIONS OF SMCRA AND THE NEW MEXICO PROGRAM THAT SJCC

    HAS VIOLATED AND CONTINUES TO VIOLATE.

    SMCRA requires each permittee to minimize disturbances to (1) the prevailing hydrologic

    balance at the mine-site and in associated offsite areas and (2) the quality and quantity of water in

    surface and ground water systems both during and after surface coal mining operations and during

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    reclamation. 30 U.S.C. 1265(b)(10). SMCRA requires that each permittee achieve these goals by

    (i) avoiding acid or other toxic mine drainage, (ii) preventing or removing water from contact with

    toxic producing deposits, and (iii) treating drainage to reduce toxic content which adversely affects

    downstream water upon being released to water courses. Id.

    The New Mexico program implements SMCRAs hydrologic protection requirements

    through rules and regulations that require each New Mexico permittee to:

    (1) plan and conduct surface coal mining operations to prevent material damage to the

    hydrologic balance outside of the permit area, NMAC 19.8.20.2009(A) (emphasis

    supplied);

    (2) avoid violation of any federal or state water quality statute, regulation, standard, or

    effluent limitation, NMAC 19.8.20.2009(C);

    (3) minimize water pollution and use treatment facilities where necessary to control

    water pollution, NMAC 19.8.20.2009(D);

    (4) prevent waters draining off of the regraded area of each mine from (a) exceeding

    baseline values of pollutants listed in NMAC 19.8.20.2009(E)(2)(a) or (E)(3)(a),

    (b) creating an increase in sediment load into the receiving streams; ( c ) creating any

    environmental harm or threat to public health and safety; or (d) degrading, polluting,

    or otherwise diminishing the characteristics of existing streams and drainages so as

    to cause imminent environmental harm to fish and wildlife habitats, NMAC

    19.8.20.2009(E)(2);

    (5) ensure that discharges of water from areas disturbed by surface mining activities and

    underground mining activities comply with all applicable state and federal

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    water-quality laws and regulations and with the effluent limitations for coal mining

    promulgated by the U.S. environmental protection agency set forth in 40 CFR Part

    434, NMAC 19.8.20.2010(A)(8);

    (6) install, operate, and maintain adequate facilities to treat any water discharged from

    the disturbed area so that it complies with all federal and state laws and regulations

    and the limitations of NMAC 19.8.20, NMAC 19.8.20.2010(C);

    (7) design, construct, and maintain all stream diversions to prevent material damage

    outside the permit area and to assure the safety of the public, NMAC

    19.8.20.2011(A), 19.8.20.2012(A)(1);

    (8) place backfilled materials so as to (a) minimize contamination of ground water

    systems with toxic or otherwise harmful mine drainage, (b) minimize adverse effects

    of mining on ground water systems outside the permit area, and (c) support approved

    postmining land uses, NMAC 19.8.20.2018(A); and

    (9) utilize pits, cuts, and other mine excavation or disturbances in such manner as to

    prevent or control discharge of toxic or otherwise harmful mine drainage waters into

    ground water systems and to prevent adverse impacts on such ground water systems

    or on approved postmining land uses, NMAC 19.8.20.2018(B) (emphasis

    supplied).

    SJCC has violated each of the provisions cited above.

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    II. THE ACTS OR OMISSIONS WHICH CONSTITUTE THE ALLEGED

    VIOLATIONS BY SAN JUAN COAL COMPANY.

    A. SJCC Has Placed Coal Combustion Waste in Mined Areas in a Manner That

    Has Polluted Ground water and Caused Material Damage to the Hydrologic

    Balance Outside SJCCs Permit Area.

    SJCC has used unlined mining pits, cuts, or other excavations to store coal combustion waste

    (CCW), including precipitator ash, bottom ash, waste water sludge, flue gas desulfurization sludge,

    and other power plant wastes, in a manner that has failed to minimize contamination of ground water

    systems with toxic or otherwise harmful mine drainage, failed to prevent adverse effects of mining

    on ground water systems outside the permit area, and failed to support approved postmining land

    uses. For example, but not by way of limitation, SJCC used CCW to fill or backfill disturbed areas

    in and adjacent to the historic channel of Shumway Arroyo upgradient of Well L in SJCCs ground

    water monitoring scheme. See 2009 SJCC Permit Renewal Application, Exhibit 907. B(4)-1 (Map

    of Surface & Ground water Monitoring Locations showing, inter alia, the locations of Well GL

    and of CCB Pits on SJCCs permit area). Similarly, SJCC or its predecessor used CCW to fill or

    backfill disturbed areas adjacent to the location of current ground water monitoring Well D. Well

    D is located upgradient of both the Shumway Diversion channel and the lower portion of Westwater

    Arroyo, which extends from its confluence with Shumway Diversion to its confluence with the

    historic channel of Shumway Arroyo. Id. (showing the locations of Well GD and adjacent CCB

    Pits).

    At a minimum, SJCCs failures with respect to the ground water protection requirements of

    SMCRA and the New Mexico program are evident in data on the quality of ground water drawn

    from Well D and Well L. SJCC has established and maintained Wells D and L to detect mining-

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    1 Sierra Club has completed its analysis of pollution to date of ground water at Wells D and

    L with respect to selenium, boron, chloride, and sulfate. Sierra Club continues to analyze the

    available data on concentrations of other pollutants at those locations, including but not limited to

    uranium, radium, manganese, arsenic, cadmium, lead, chromium, iron, magnesium, phenols, and

    sodium. Sierra Club asserts the right to demonstrate in its intended civil action that SJCCs

    violations of SMCRA and the New Mexico program also occur due to pollution of ground water at

    Wells D or L by any other contaminant for which there exists an applicable New Mexico ground

    water standard.

    -5-

    related hydrologic impacts outside the permit area, including impact from placement of CCW in

    areas upgradient of either of those wells. See Permit Application, Section 907.B(4)(i) Ground

    water Monitoring Plan at 907-12.

    The tables and graphs on the following pages present and summarize available data

    concerning concentrations of selenium and boron in Well D over the past 36 years and

    concentrations of selenium, chloride, and sulfate in Well L over the past 30 years. The applicable

    New Mexico ground water quality standards for these pollutants are: selenium 0.05 mg/l; boron

    0.75 mg/l, chloride 250.0 mg/l, and sulfate 600.0 mg/l. See 20.6.2.3103 NMAC.1

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    Sample Date Selenium NMED/gwb Boron NMED/gwb

    9/14/2009 0.105 0.05 2.00 0.75

    3/19/09 8:35 AM 0.05 1.80 0.75

    9/17/08 1:02 PM 0.178 0.05 1.80 0.75

    3/11/08 8:02 AM 0.034 0.05 2.10 0.75

    12/3/07 9:29 AM 0.05 0.759/27/07 12:00 PM 0.091 0.05 2.30 0.75

    3/28/07 2:28 PM 0.082 0.05 2.50 0.75

    9/29/06 2:28 PM 0.117 0.05 2.80 0.75

    6/5/06 2:02 PM 0.05 0.75

    3/16/06 9:42 AM 0.145 0.05 2.30 0.75

    9/30/05 9:56 AM 0.104 0.05 1.70 0.75

    3/8/05 9:51 AM 0.117 0.05 1.90 0.75

    12/28/04 3:01 PM 0.133 0.05 2.00 0.75

    3/19/04 2:15 PM 0.153 0.05 1.30 0.75

    12/15/03 2:15 PM 0.066 0.05 1.30 0.75

    7/10/03 10:24 AM 0.100 0.05 1.30 0.75

    3/12/03 10:48 AM 0.090 0.05 1.40 0.75

    12/16/02 12:00 AM 0.008 0.05 1.50 0.75

    9/27/02 12:00 AM 0.094 0.05 0.60 0.75

    6/18/02 2:00 AM 0.001 0.05 0.10 0.75

    3/20/02 12:00 AM 0.160 0.05 1.10 0.75

    12/12/01 12:00 AM 0.200 0.05 1.50 0.75

    9/25/01 12:00 AM 0.200 0.05 1.60 0.75

    6/26/01 12:00 AM 0.060 0.05 1.40 0.75

    3/19/01 12:00 AM 0.130 0.05 1.00 0.75

    12/18/00 12:00 AM 0.0100.05

    1.50 0.759/26/00 12:00 AM 0.200 0.05 10.00 0.75

    6/23/00 12:00 AM 0.005 0.05 1.70 0.75

    6/21/00 12:00 AM 0.05 1.20 0.75

    3/29/00 12:00 AM 1.00 0.05 1.10 0.75

    12/15/99 12:00 AM 0.017 0.05 1.20 0.75

    9/28/99 12:00 AM 0.108 0.05 1.44 0.75

    3/30/99 12:00 AM 0.060 0.05 1.42 0.75

    12/16/98 12:00 AM 0.070 0.05 1.56 0.75

    7/8/98 12:00 AM 0.068 0.05 1.03 0.75

    3/30/98 12:00 AM 0.005 0.05 1.20 0.75

    12/18/97 12:00 AM 0.027 0.05 1.67 0.75

    6/26/97 12:00 AM 0.050 0.05 0.01 0.75

    6/25/97 12:00 AM 0.019 0.05 1.83 0.75

    3/20/97 12:00 AM 0.010 0.05 1.13 0.75

    12/31/96 12:00 AM 0.018 0.05 1.10 0.75

    9/27/96 12:00 AM 0.052 0.05 1.08 0.75

    6/13/96 12:00 AM 0.041 0.05 0.91 0.75

    3/12/96 12:00 AM 0.067 0.05 1.27 0.75

    12/11/95 12:00 AM 0.062 0.05 1.23 0.75

    San Juan Coal Mine Well D Sampling Table

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    Sample Date Selenium NMED/gwb Boron NMED/gwb

    San Juan Coal Mine Well D Sampling Table

    9/6/95 12:00 AM 0.005 0.05 1.03 0.75

    6/20/95 1:00 AM 0.020 0.05 0.96 0.75

    6/20/95 12:00 AM 0.05 0.75

    3/9/95 12:00 AM 0.080 0.05 1.16 0.75

    12/8/94 12:00 AM 0.032 0.05 1.90 0.759/12/94 12:00 AM 0.009 0.05 0.97 0.75

    6/16/94 12:00 AM 0.038 0.05 0.97 0.75

    3/15/94 12:00 AM 0.057 0.05 1.07 0.75

    12/15/93 12:00 AM 0.083 0.05 1.34 0.75

    9/9/93 12:00 AM 0.05 1.10 0.75

    6/17/93 12:00 AM 0.010 0.05 1.16 0.75

    3/17/93 12:00 AM 0.076 0.05 1.22 0.75

    12/9/92 12:00 AM 0.004 0.05 0.97 0.75

    9/15/92 12:00 AM 0.031 0.05 1.26 0.75

    6/8/92 12:00 AM 0.048 0.05 1.08 0.75

    3/26/92 12:00 AM 0.051 0.05 1.00 0.75

    12/16/91 12:00 AM 0.056 0.05 1.22 0.75

    9/4/91 12:00 AM 0.046 0.05 1.28 0.75

    6/11/91 1:00 AM 0.060 0.05 0.86 0.75

    6/11/91 12:00 AM 0.05 0.75

    3/27/91 12:00 AM 0.052 0.05 1.18 0.75

    12/20/90 12:00 AM 0.003 0.05 1.15 0.75

    10/30/90 12:00 AM 0.05 1.06 0.75

    6/7/90 12:00 AM 0.003 0.05 1.00 0.75

    3/6/90 12:00 AM 0.001 0.05 0.86 0.75

    12/5/89 12:00 AM 0.0050.05

    0.79 0.759/6/89 12:00 AM 0.005 0.05 0.93 0.75

    5/31/89 12:00 AM 0.005 0.05 0.73 0.75

    3/13/89 12:00 AM 0.006 0.05 1.01 0.75

    7/5/88 12:00 AM 0.009 0.05 0.95 0.75

    12/12/87 12:00 AM 0.004 0.05 1.05 0.75

    6/19/87 12:00 AM 0.052 0.05 1.20 0.75

    1/14/87 12:00 AM 0.004 0.05 1.15 0.75

    10/26/86 12:00 AM 0.001 0.05 1.12 0.75

    12/2/81 11:44 AM 0.05 1.00 0.75

    9/23/81 10:44 AM 0.05 0.70 0.75

    6/24/81 9:44 AM 0.05 1.40 0.75

    4/1/81 12:00 AM 0.05 1.00 0.75

    12/3/80 2:02 PM 0.05 1.70 0.75

    9/17/80 2:01 PM 0.05 0.50 0.75

    6/15/80 2:57 PM 0.010 0.05 1.00 0.75

    11/28/79 12:43 PM 0.05 1.00 0.75

    10/3/79 12:43 PM 0.05 1.00 0.75

    8/14/79 11:43 AM 0.05 0.02 0.75

    4/5/79 11:39 AM 0.010 0.05 1.10 0.75

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    Sample Date Selenium NMED/gwb Boron NMED/gwb

    San Juan Coal Mine Well D Sampling Table

    4/10/75 6:04 PM 0.010 0.05 1.20 0.75

    3/10/75 7:04 PM 0.010 0.05 0.80 0.75

    1/29/75 8:47 PM 0.010 0.05 0.35 0.75

    12/23/74 7:47 PM 0.010 0.05 0.16 0.75

    12/10/73 1:47 PM 0.150 0.05 1.50 0.759/6/73 1:47 PM 0.010 0.05 2.30 0.75

    7/24/73 1:47 PM 0.010 0.05 0.25 0.75

    Selenium value of 1.00 on 3/29/2000 was substituted with a plot value of .5 only to allow the viewer to see the lower concentrations.

    The Selenium value of 1.00 is the correct concentration for that date.

    The Boron value of 10. on 9/26/2000 was substituted with a plot value of .4 only to allow the viewer to see the lower concentrations.

    The Boron value of 10. is the correct concentration for that date.

    All data from ENMRD files except 9/14/2009 taken by Four Corners Geosciences

    NMED/gwb New Mexico Environment Department Ground Water Bureau

    Notes:

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    0.000.50

    1.00

    1.50

    2.00

    2.50

    3.00

    3.50

    4.00

    4.50

    C

    oncentrationinmg/L

    Well D Boron

    Boron

    NMED/gwb

    0.0000.0500.100

    0.1500.2000.2500.300

    0.3500.4000.450

    0.500

    Concentrationinmg/L

    Well D Selenium

    Selenium

    NMED/gwb

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    Well L Contaminant Plotting Table

    Sample Date Sulfate NMED/gwb Selenium NMED/gwb Chloride NMED/gwb

    9/14/2009 53000 600 0.06 0.05 7400 250

    3/19/2009 40000 600 0.13 0.05 6000 250

    9/17/2008 42000 600 0.039 0.05 6300 250

    7/17/2008 39100 600 0.018 0.05 6670 250

    3/11/2008 600 0.05 250

    3/11/2008 43000 600 0.016 0.05 5200 250

    12/3/2007 600 0.05 250

    9/27/2007 48000 600 0.05 0.05 6900 250

    3/28/2007 39100 600 0.046 0.05 6000 250

    3/28/2007 600 0.05 250

    9/29/2006 600 0.05 250

    9/28/2006 44000 600 0.068 0.05 5600 250

    6/5/2006 600 0.05 250

    3/15/2006 47000 600 0.15 0.05 6200 250

    9/30/2005 44000 600 0.058 0.05 6350 250

    9/30/2005 44000 600 0.058 0.05 6350 250

    3/8/2005 43000 600 0.029 0.05 6450 250

    12/28/2004 52000 600 0.042 0.05 6500 250

    3/18/2004 51000 600 0.06 0.05 6400 2509/29/2003 42500 600 0.001 0.05 5100 250

    7/11/2003 47000 600 0.001 0.05 5450 250

    9/26/2002 42000 600 0.001 0.05 6260 250

    6/18/2002 40000 600 0.002 0.05 6200 250

    12/12/2001 39800 600 0.4 0.05 6500 250

    9/25/2001 41000 600 0.1 0.05 6300 250

    6/28/2001 39000 600 0.2 0.05 6300 250

    3/19/2001 41000 600 0.5 0.05 6200 250

    12/18/2000 39000 600 0.01 0.05 5850 250

    9/26/2000 37000 600 0.2 0.05 5600 250

    6/21/2000 42000 600 0.1 0.05 5950 250

    3/29/2000 40000 600 1 0.05 5700 250

    12/15/1999 41000 600 0.5 0.05 6000 250

    9/28/1999 37300 600 0.005 0.05 5600 250

    6/23/1999 36300 600 0.005 0.05 5690 250

    3/29/1999 38800 600 0.005 0.05 5630 250

    12/15/1998 42000 600 0.005 0.05 5600 250

    9/16/1998 32700 600 0.005 0.05 4700 250

    6/25/1998 33800 600 0.005 0.05 5550 250

    3/30/1998 29800 600 0.005 0.05 4750 250

    12/18/1997 34300 600 0.005 0.05 5300 250

    9/25/1997 39000 600 0.005 0.05 5260 250

    6/26/1997 36356 600 0.005 0.05 250

    3/20/1997 31600 600 0.005 0.05 4636 250

    12/31/1996 33216 600 0.005 0.05 5241 2509/27/1996 33500 600 0.005 0.05 4910 250

    6/13/1996 33100 600 0.005 0.05 4850 250

    3/12/1996 32800 600 0.005 0.05 6200 250

    12/11/1995 27800 600 0.005 0.05 4100 250

    9/6/1995 28800 600 0.005 0.05 3690 250

    6/20/1995 28400 600 0.005 0.05 4000 250

    3/9/1995 30200 600 0.005 0.05 4490 250

    12/8/1994 27100 600 0.005 0.05 3710 250

    9/12/1994 28800 600 0.005 0.05 3940 250

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    Well L Contaminant Plotting Table

    Sample Date Sulfate NMED/gwb Selenium NMED/gwb Chloride NMED/gwb

    6/16/1994 26000 600 0.001 0.05 4040 250

    3/16/1994 28000 600 0.001 0.05 3520 250

    12/15/1993 28500 600 0.001 0.05 3380 250

    9/9/1993 21800 600 0.001 0.05 3540 250

    6/17/1993 21400 600 0.01 0.05 3460 250

    3/17/1993 24600 600 0.001 0.05 3360 250

    12/9/1992 22500 600 0.001 0.05 3400 250

    9/15/1992 25200 600 0.001 0.05 3340 250

    6/8/1992 23800 600 0.001 0.05 2900 250

    3/26/1992 21500 600 0.001 0.05 3100 250

    12/16/1991 23000 600 0.001 0.05 2900 250

    9/4/1991 24500 600 0.001 0.05 2920 250

    6/11/1991 18400 600 0.001 0.05 2650 250

    6/11/1991 22570 600 0.05 2920 250

    3/27/1991 22900 600 0.001 0.05 2860 250

    12/20/1990 24370 600 0.05 2920 250

    9/13/1990 24460 600 0.05 2440 250

    6/7/1990 23327.9 600 0.05 2762 250

    3/6/1990 23430.81 600 0.05 2817 25012/5/1989 22340 600 0.005 0.05 2602 250

    9/6/1989 23620 600 0.005 0.05 2701 250

    5/31/1989 22707 600 0.005 0.05 2754 250

    3/13/1989 22447 600 0.005 0.05 2588 250

    6/27/1988 22180 600 0.005 0.05 2620 250

    12/12/1987 18800 600 0.001 0.05 6320 250

    6/19/1987 16700 600 0.002 0.05 6150 250

    1/14/1987 20400 600 0.001 0.05 7050 250

    12/2/1981 15600 600 0.05 2600 250

    9/23/1981 19670 600 0.05 2480 250

    6/24/1981 20500 600 0.05 2540 250

    4/1/1981 20878 600 0.05 2620 250

    12/3/1980 21200 600 0.05 2800 250

    9/17/1980 21200 600 0.05 2600 250

    6/5/1980 20900 600 0.05 2700 250

    3/6/1980 21139 600 0.01 0.05 1874 250

    11/29/1979 25000 600 0.05 3060 250

    10/3/1979 22500 600 0.05 3280 250

    NOTES:

    The value of 1.0 for Chloride on 6/26/1997 appears to be a recording error. All other Chloride values for

    well L range from 1874 to 7400 mg/L. The value 1. is not plotted for this date.

    All data obtained from ENMRD files except for 9/14/09 taken by Four Corners Geosciences

    NMED/gwb New Mexico Environment Department Ground Water Bureau

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    12

    0

    1000

    2000

    3000

    4000

    5000

    6000

    7000

    8000

    Concentrationinmg/L

    Well L Chloride

    Chloride

    NMED/gwb

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    0

    0.1

    0.2

    0.3

    0.4

    0.5

    0.6

    0.7

    0.8

    0.9

    1

    Concentrationinmg/L

    Selenium

    NMED/gwb

    Well L Selenium

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    0

    10000

    20000

    30000

    40000

    50000

    60000

    Concentrationinmg/L

    Well L Sulfate

    Sulfate

    NMED/gwb

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    The only possible cause of the increasing pollutant concentrations in ground water drawn

    from Well L is leaching of pollutants from CCW, followed by transport off the permit area either

    by ground water movement, diffusion, or both. Although ground water drawn from Well D may also

    be affected by mine spoils and runoff from SJCCs coal storage area, placement of CCW in mined

    areas upgradient of Well D has contributed to exceedences of applicable ground water protection

    standards at that location. Ground water at Well D flows in a southerly direction through the alluvial

    aquifer and mine spoils to Shumway Diversion and the historic channel of Westwater Arroyo.

    Polluted ground water from Well D then travels through the alluvial aquifer or as surface water to

    the point where Westwater/Shumway Arroyo exits the permit area.

    Thus, CCW placement has caused or contributed to material damage to the hydrologic

    balance outside the permit area and has otherwise violated the applicable hydrologic protection

    regulations cited in the previous section of this notice. CCW deposits at SJCCs mine continue to

    do so. Despite the existence of this mine-related degradation of the hydrologic regime, SJCC has

    failed to establish or use comprehensive treatment facilities to control the water pollution in

    question.

    B. SJCCs Operations Have Introduced Additional Water to the Hydrologic

    Regime and Created Conditions That Allow the Additional Water to Become

    Polluted, Discharge to the Shumway/Westwater Arroyo System, and Cause or

    Contribute to Material Damage to the Hydrologic Balance Outside SJCCs

    Permit Area.

    In conducting surface coal mining and reclamation operations, SJCC has added water to lands

    abutting a desert arroyo system. SJCC has done so in a variety of ways, including but not limited

    to the watering of coal storage areas and haul roads. The adjacent power plant may also have added

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    additional water to the system through leaks in evaporation ponds, infiltration of water used in

    transporting coal from SJCCs stockpiles to the power plant, or other activities.

    Prior to the advent of industrial activity in the area, the surrounding desert arroyo system

    transmitted water only in direct, immediate response to precipitation events. Since the

    commencement of industrial activity, however, SJCCs mine, the adjacent power plant, or both have

    created an elevated water table in the vicinity of SJCCs coal stockpile and the power plants eastern

    evaporation ponds.

    To facilitate mining coal in the vicinity of the historic channel of Shumway Arroyo, SJCC

    has designed, constructed, operated, and maintained a diversion channel for that stream (Shumway

    Diversion). The diversion channel intercepts the artificially elevated water table in the area of

    SJCCs coal storage facility.

    As a direct result, flowing . . . [w]ater exists within the Shumway Diversion for at least six

    months of the year. 2009 Permit Application, Section 907.A(1) at 907-3; 2004 Permit Application,

    Section 907.A(1) at 907-3. Despite repeatedly acknowledging this fact in permit applications over

    at least the past five years, SJCC has failed to minimize the resulting disturbances to the prevailing

    hydrologic balance at the mine-site and in associated offsite areas. As a result, Shumway Diversion

    has caused and continues to cause significant degradation of the quality and quantity of water

    downgradient of SJCCs mine.

    Put another way, SJCC has designed, constructed, operated, and maintained Shumway

    Diversion and adjacent surface coal mining operations in a manner that adds water to the hydrologic

    regime but (a) fails to avoid toxic mine drainage, (b) fails to prevent or remove water from contact

    with toxic producing deposits, or (c) fails to treat drainage to reduce toxic content which adversely

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    -17-

    affects downstream water upon being released to water courses. More specifically, SJCC has

    designed, constructed, operated, and maintained Shumway Diversion and surface coal mining

    operations located adjacent to and downgradient of that diversion in a manner which:

    (1) causes or contributes to material damage to the hydrologic balance outside of the

    permit area by discharging polluted water from the permit area in Shumway Arroyo

    and through the alluvial aquifer at times when, upgradient of the permit area,

    Shumway Arroyo and Westwater Arroyo cumulatively either have no flow or have

    significantly less flow than they do downgradient of the permit area;

    (2) violates applicable federal or state water quality statutes, regulations, standards, or

    effluent limitations by discharging polluted water from the permit area through

    Shumway Arroyo, Westwater Arroyo, or their alluvial aquifers at times when,

    upgradient of the permit area, Shumway Arroyo and Westwater Arroyo cumulatively

    either have no flow or have significantly less flow than they do downgradient of the

    permit area;

    (3) causes or contributes to water pollution by discharging polluted water through

    Shumway Arroyo or Westwater Arroyo when, upgradient of the permit area,

    Shumway Arroyo and Westwater Arroyo cumulatively either have no flow or have

    significantly less flow than they do downgradient of the permit area;

    (4) fails to use treatment facilities to control water pollution resulting from the discharge

    of polluted water through Shumway Arroyo, Westwater Arroyo, or their alluvial

    aquifers when, upgradient of the permit area, Shumway Arroyo and Westwater

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    -18-

    Arroyo cumulatively either have no flow or have significantly less flow than they do

    downgradient of the permit area;

    (5) allows waters draining off of the regraded area of SJCCs mine (a) to exceed baseline

    values of pollutants listed in NMAC 19.8.20.2009(E)(2)(a) or (E)(3)(a), (b) to

    create an increase in sediment load into the receiving streams; (c) to cause or

    contribute to environmental harm by polluting water in the downgradient portion of

    Shumway Arroyo and thus impairing the use of that water or associated ground water

    for human consumption, irrigation, or livestock watering; or (d) to degrade, pollute,

    or otherwise diminish the characteristics of water in the downgradient portion of

    Shumway Arroyo and in adjacent portions of the San Juan River alluvial aquifer, so

    as to cause imminent environmental harm to fish and wildlife habitats;

    (6) discharges water from areas disturbed by surface mining activities (including but not

    limited to coal storage and placement of CCW), which water violates applicable state

    and federal water-quality laws and regulations by continuously, regularly, or

    intermittently discharging polluted water from the permit area through Shumway

    Arroyo, Westwater Arroyo, or their alluvial aquifers at times when Shumway Arroyo

    and Westwater Arroyo cumulatively either have no flow or have significantly less

    flow than they do downgradient of the permit area;

    (7) fails to provide adequate facilities to treat water discharged from the disturbed area

    through Shumway Arroyo or Westwater Arroyo at times when Shumway Arroyo and

    Westwater Arroyo cumulatively either have no flow or have significantly less flow

    than they do downgradient of the permit area, so as to ensure that such water

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    2 Additionally, the results of surface water monitoring by the New Mexico regulatory authority,

    SJCC, or both, at surface water monitoring station 006, as reported on the regulatory authoritys

    website, establish an instance in which concentration of dissolved selenium exceeded the applicablenumeric water quality standard for total selenium. The regulatory authority, SJCC, or both

    frequently report a higher concentration of dissolved selenium than the concentration of total

    selenium reported in the same sample. Because the concentration of total selenium in any water

    sample is axiomatically either equal to or in excess of the concentration of dissolved selenium, the

    posted results clearly involve human error of some sort. Taking the higher of the two reported

    concentrations as the concentration of total selenium in the sample, the posted results establish

    exceedence of the New Mexico water quality standard for total selenium at station 006 on September

    9, 2005. On that date the sampling entity did not report selenium concentrations in excess of the

    applicable water quality standard at station 005, upgradient of SJCCs permit.

    Sierra Club has completed its analysis of pollution to date of surface water at the road culvert

    with respect to selenium, sodium, and total dissolved solids. Sierra Club continues to analyze the

    available data on concentrations of other pollutants at pertinent locations, including but not limited

    to uranium, radium, manganese, arsenic, cadmium, copper, lead, nickel, chromium, iron,

    magnesium, and phenols. Sierra Club asserts the right to demonstrate in its intended civil action that

    (continued...)

    -19-

    complies with all federal and state laws and regulations and the limitations of NMAC

    19.8.20; and

    (8) fails to prevent material damage outside the permit area and assure the safety of the

    public, NMAC 19.8.20.2011(A), 19.8.20.2012(A)(1).

    At a minimum, SJCCs failure to prevent material damage outside the permit area as the

    result of adding water to the hydrologic regime is apparent in the results of water samples that Sierra

    Club representatives obtained during their September 14, 2009, site visit at the road culvert

    immediately upgradient of the point at which Westwater Arroyo first exits SJCCs permit area.

    Those results, which appear on the following page, show that the water sampled at that location

    exceeded the applicable New Mexico numeric standard for surface water quality with respect to total

    selenium and the applicable narrative standards for odor, taste, and reasonable use with respect to

    sodium, chloride, sulfate, and total dissolved solids.2

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    Water Quality Exceedances at Culvert 09142009

    Sample ID Date Site Name

    RGHunt_14 20090914 -10825.812 3647.578min Culvert

    Contaminant mg/L Criteria Documentation

    Sodium 1070 see Footnotes 20.6.4.13

    injure life, property, public welfare and

    use (Narrative Standard)

    Total Selenium 0.009 0.005 Wildlife habitat

    Chloride 318 see Footnotes 20.6.4.13

    injure life, property, public welfare and

    use (Narrative Standard)

    Sulfate 2800 see Footnotes 20.6.4.13

    injure life, property, public welfare and

    use (Narrative Standard)

    TDS 5010 see Footnotes 20.6.4.13K

    injure life, property, public welfare and

    use (Narrative Standard)

    Footnotes:

    National Secondary Drinking Water Standards is 250 mg/L for both Chloride and Sulfate

    National Secondary Drinking Water Standards is 500 mg/L for Total Dissolved Solids (TDS)

    National HealthBased Drinking Water Advisories are 20 mg/L for Sodium and 500 mg/L for Sulfate

    2006 Edition,Drinking Water Standards and Health Advisories, Office of Water, US EPA, Washington, DC, August 2006

    Location

    20

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    2(...continued)

    SJCCs violations of SMCRA and the New Mexico program also occur due to pollution of surface

    water at the culvert or any surface water monitoring station by any other contaminant for which there

    exists an applicable New Mexico surface water quality standard.

    -21-

    Sierra Club representatives observed the stream of water that they sampled at the culvert

    continuing to flow from the culvert to and beyond the boundary of SJCCs permit. There were no

    observed conditions or structures between the road culvert and the permit boundary which would

    have materially reduced the pollutant concentrations observed in water sampled at the culvert before

    that water exited SJCCs permit area.

    III. INFORMATION ABOUT THE PERSON RESPONSIBLE FOR THE ALLEGED

    VIOLATIONS.

    The person responsible for the violations alleged above is San Juan Coal Company, a

    corporation. SJCCs address is P. O. Box 561, Waterflow, NM 87421. SJCCs telephone number

    is (505) 598-2000.

    IV. THE DATE, TIME, AND LOCATION OF THE ALLEGED VIOLATIONS.

    Each of the violations alleged above is a continuing violation. Each of the ground water

    violations occurs at the point where transmission of increased concentrations of each enumerated

    pollutant, whether by ground water flow, diffusion, or both, crosses SJCCs permit boundary and

    at such upgradient point, if any, at which a pollutant concentration first exceeds an applicable

    hydrologic protection standard. Each of the surface water violations occurs at the point on the permit

    area of SJCCs mine where Shumway Diversion becomes a perennial or intermittent stream, as the

    case may be. The violation continues from that point downgradient to the point at which Shumway

    Arroyo or Westwater Arroyo first exits the western boundary of SJCCs permit, and from that point

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    -22-

    at least as far downgradient as the pollution attributable to SJCCs operations causes or contributes

    to a violation of applicable water quality standards.

    Each violation relating to pollution of ground water by CCW began on the date on which a

    pollutant concentration in ground water affected by SJCCs placement of CCW first exceeded an

    applicable hydrologic protection standard or caused or contributed to such an exceedence outside

    SJCCs permit area. That date or set of dates is unknown to Sierra Club.

    Each violation relating to water that SJCCs operations have added to the hydrologic balance

    began on the date on which Shumway Arroyo first discharged polluted water from the permit area

    after approval and issuance of SJCCs mining permit, other than in direct and immediate response

    to a precipitation event. That date is unknown to Sierra Club.

    Each violation has recurred constantly, regularly, or intermittently thereafter, whenever

    Shumway Arroyo discharges polluted water from the permit area and there either is no flow or

    significantly less flow in Shumway Arroyo and Westwater Arroyo upgradient of the permit area.

    Sierra Club representatives most recently observed instances of each of the violations alleged above

    either on September 14, 2009, during their inspection of SJCCs mine, or during their subsequent

    analysis of water quality test results with respect to samples obtained during that inspection.

    V. REQUIRED ADDITIONAL INFORMATION.

    Sierra Clubs address is 85 Second Street, 2d Floor, San Francisco, California 94105-3441;

    its telephone number is (415) 977-5680. The names, addresses, and telephone numbers of Sierra

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    -23-

    Clubs legal counsel are shown below. Sierra Club requests that any person receiving this notice

    direct all inquiries to the undersigned legal counsel.

    Dated November 19, 2009 SIERRA CLUB

    -By Counsel-

    Walton D. Morris, Jr.

    Morris Law Office, P.C.

    1901 Pheasant Lane

    Charlottesville, Virginia 22901

    Telephone (434) 293-6616

    Fax (434) 293-2811

    E-mail: [email protected]