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About the Mining Act of 1872

Following the boom of mineral discoveries in the west such as the California Gold Rush, the General Mining Act of 1872 was passed by President Ulysses S. Grant to promote settlement and natural resource development in the west. Despite outdated terms, such as charging claimants a “mineral patent” to mine land at no more than $5 per acre, this law continues to govern mineral exploration and extraction in the U.S. today.

SEC. 2319. All valuable mineral deposits in lands belonging to the United States, both surveyed and unsurveyed, are hereby declared to be free and open to exploration and purchase… Click here for the full text of the 1872 Mining Act

Articles and Reports about the Mining Act

Recommended Actions for Management Plans

OHA recommends that Ecology require Crown to take the following actions that would help clarify monitoring and closure requirements and lead to the eventual restoration of mine site water quality:


Add monitoring wells to the underground mine: There is currently only one monitoring point in each of the two zones to analyze water quality changes in the Buckhorn underground mine during closure. More monitoring is needed to understand how recirculation is affecting mine water quality, especially in a fractured bedrock setting. Water quality monitoring wells should be added to the more distant portions of the underground mine (not along the preferential pathway) to evaluate the effectiveness of recirculation during closure.

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Recommended Actions for Permit Violations

Effectiveness of measures taken: Ecology should insist that Crown provide the agency with a critical investigation into the effectiveness of each mitigation measure it has implemented as part of the settlement of the July 2012 penalty for water quality violations. This evaluation was required by a July 19, 2016 administrative order but was never produced by the company. Evaluations are necessary to better understand the successes and failures of past actions and to help guide future actions. Ecology must make sure its role as regulator is not undermined by the company ignoring its authority with no consequences.

Communication about Violations: Each month, Crown/Kinross Discharge Monitoring Reports contain numerous violations. OHA recommends that Ecology inform the mining company that the violation(s) can be subject to significant penalties, and that the agency order corrective action. Ecology should administer its regulatory responsibility to ensure that Crown/Kinross follows through on orders and commitments to contain mine contaminants.

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World Wetlands Day 2019

Wetlands around the world protect communities while helping fight climate change

As the world grapples with climate change, those commemorating World Wetlands Day Feb. 2 are highlighting the importance of restoring, conserving, and wisely using wetlands because they can help reduce floods, relieve droughts, and buffer coastlines from extreme weather.

In the state of Washington, we work every day to protect and manage wetlands. The environmental and economic benefits they provide nature, our communities, and way of life are immeasurable…

To help celebrate World Wetlands Day, the WA State Department of Ecology selected the Triple Creek project to feature on their blog. Click here to read the full article.

Landowners Support Beavers for Restoration

In 1980, a group of like-minded individuals purchased over 500 acres of land along Myers Creek north of Chesaw, on a site now known as Triple Creek. They formed an intentional community based on simple living and sustainable paths for securing food and shelter. Several households now live on this Okanogan Highlands landscape of forests, meadows, wetlands, and riparian areas. A primary goal of the community is improving and restoring wildlife habitat for native species. Members have developed a forest management plan, rehabilitated overgrazed pastures, and reduced noxious weeds, thus reestablishing native plants. By engaging with local non-profits and agencies for wetland restoration, the community is creating a legacy to benefit future generations…

Read more about the role of the land stewards and the development of this collaboration in this 2015 IRIS (Initiative for Rural Innovation & Stewardship) Success Supplement excerpt.

Wetland Protection in Upper Wauconda

LandownerCollaboration - OHA-OkanoganHighlandsAlliance-Restoration-LandownerSupport-LeeJohnson_PineCheeMaintenance.jpg

In November 2013, OHA approved an application for reimbursement for Wauconda landowner, Lee Johnson. Lee sought reimbursement for expenses for fences to protect a unique and exceptional wetland that he recently purchased.

Having lived adjacent to the wetland for over 30 years, Lee has built and maintained a fence that protects this resource, long before he actually purchased the wetland.

The protected area includes approximately 25 acres of wetland and forest fringe, laying north of Bunch Road at 4,000 feet elevation.

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Articles about the Preserve

Click to view the Fall 2014 Lost Lake Preserve update
Click to view an article about Lost Lake in the Washington State Lake Protection Association (WALPA) newsletter

OHA’s Recommendations for Buckhorn Mine Plans

Note: This text still needs to be edited (See Google Drive)

OHA recommends that Ecology require Crown to take the following actions that would help clarify monitoring and closure requirements and lead to the eventual restoration of mine site water quality:

  • Add monitoring wells to the underground mine. One monitoring point to measure changes in two zones of the Buckhorn underground mine during closure is insufficient to understand how recirculation is affecting mine water quality, especially in a fractured bedrock setting. Water quality monitoring wells should be added to the distal portions of the underground mine (not along the preferential pathway) to evaluate the effectiveness of recirculation during closure.
  • Modify the HCP. A modified HCP should include the issues discussed in Ecology’s approval letter, especially a requirement to have all monitoring locations on the site meet applicable permit limits for five freshets after recirculation, dewatering, and treatment have stopped. During this time, the treatment plant, dewatering, and recirculation should be able to be restarted if permit limits are not met. The HCP should clarify that all monitoring locations on the site should meet permit limits by the end of closure, including those inside the capture zone.
  • Require a closure AMP. A separate closure AMP should be required to address changes in water quality, stream flows, and groundwater elevations during closure and post-closure. The closure AMP should include monitoring locations and criteria, trigger levels, mitigation measures to be taken, responsibilities, and evaluation of mitigation effectiveness. The closure AMP should also include contingencies that expand the time period and potentially restart water treatment if water quality degrades during the five-year period of the closure phase after treatment has ceased and during the ten-year period of post closure phase. The trigger for adaptive management action should be a comparison to permit limits rather than historical concentrations or trends. Finally, Ecology should require that all water on the site, including areas inside the former capture zone, meets NPDES permit limits at the end of closure.
  • Require a closure HMP. A Hydrologic Monitoring Plan is needed for closure. Currently none exists. The closure HMP should include descriptions of hydrologic and water quality monitoring, including parameters, frequency, and locations, during closure and post-closure periods. A decrease in frequency between Phases 1 and 2 of closure is not warranted.
  • Require a map showing underground workings, wells, and flow directions during closure: Ecology should require Crown/Kinross to create a 3D representation showing the location of the recirculation inflow pipe and outflow well, the sampling location for the Gold Bowl sump, and the remainder of the Gold Bowl workings. The location of the inflow pipe and outflow well for the Southwest Zone and the location of the Southwest Zone sump should also be depicted in a 3D graphic. Expected flow directions in the underground mine with and without pumping should also be included. And add hydrologic plug.

Problems with Closure of the Buckhorn Mine

The plans for mine closure have been written by the mining company in such a way that there is little to no accountability. Many years in the future, regulators and mining company personnel—who are not currently involved with the Buckhorn Mine closure process—will have to manage the mine and will base their actions on the directions provided in the closure documents (see Plans ). Ecology should ensure that the plans are clear, current, and contain the best information and guidance possible.
There is no plan to determine the pathways of mine contaminants that are currently escaping the capture and treatment system, so that pollution can be reduced and/or eliminated. The closure documents talk about working with Ecology but fail to provide specific actions that would mitigate the contamination escaping capture or any mechanism to determine if mitigation is effective.


The main activity of closure is recirculating water in the underground mine. This involves pumping polluted mine water from the mine through the treatment facility and discharging it back into the mountain. Over time, this would likely improve water quality; however, this activity would draw down the water table each year to accommodate the spring freshet. This runs contrary to the strategy that was analyzed and reviewed when the mine was originally planned. The Environmental Impact Statement states that the Gold Bowl Zone is expected to flood within a few years after cessation of mining, thus limiting exposure of the reactive rock that is already found in higher proportion there.


A portion of the waste rock from blasting the Buckhorn Mine was identified as Potentially Acid Generating (PAG), or capable of forming acid that can then leach metals and lead to degradation of aquatic resources. As a way of preventing the PAG rock from forming acid, it was placed in the Gold Bowl section of the underground mine, which will be allowed to flood, minimizing oxidation and preventing the sulfide rock from becoming acidic. Unfortunately, Ecology has approved a Closure Plan that includes lowering the water level in the mine each spring to accommodate spring runoff. The drawdown will expose PAG rock and release additional pollutants into the groundwater. Exposing PAG rock increases the risk of triggering acid mine drainage, which would further degrade water quality on Buckhorn Mountain.


The Closure Plan approval letter includes the prediction that five freshets will be adequate to return the site to natural hydrologic function. It states that Ecology expects the water treatment and recirculation facilities to remain functional during that time. Voicing agency expectations does not provide the public with protection. An expectation is not a requirement. Ecology should require a plan that the mining company will follow if water quality degrades, and should provide clear criteria for when the treatment facilities may be removed. The current approval letter implies that facilities could be removed after five freshets. What if the water still needs treatment at that time? The Closure Plan mentions using adaptive management, but there are no specific benchmarks, timelines, or actions. Adaptive management is a structured decision making process that takes into account the uncertainty inherent in natural resource management. There should be a Closure Adaptive Management Plan that outlines the steps that will be triggered by various potential outcomes. In addition to providing requirements, Ecology must define what natural hydrologic function means.


The Closure Plan uses water quality and groundwater levels to define the post-closure period; as a result, the actual timeframe for this period is fluid. Since groundwater in the region has significant seasonal variation, groundwater level is not an appropriate criteria. Water quality should be used — but needs adaptive management contingencies if water quality degrades.


Long-term water quality may be affected by seepage of poor-quality water from the Damaged Rock Zone located above the water table. This probability is not considered in the Closure Plan and is a significant, unacceptable omission.


The mine’s discharge permit requires various mine-related plans (adaptive management and hydrologic monitoring) be updated to reflect current conditions. Ecology must hold the mining company accountable for these updated plans.


Monitoring should continue until permit water quality is maintained continuously for 10 years.

Water Quality Contamination

Sulfates at the Buckhorn mine
Sulfates at the Buckhorn mine (NLF-3 wells)

The red dashed line in the above graph shows the allowable (2014 permit) level of sulfate. The other dashed lines show the general trend of sulfate levels in various monitoring locations.

These monitoring wells are located in a fault downgradient from the mine, just outside the capture zone, which is supposed to capture all mine contaminants. Sulfate concentrations in all these monitoring wells (MW) are still increasing. Many values in MW-14 and MW-2R even exceeded the State groundwater standard (250 mg/L — a much higher level than the 69.5 mg/L allowed by the permit). Although MW-14, which is closest to Gold Bowl Creek, had the highest peak concentrations, the recent overall trend in that well could be decreasing slightly.

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