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Post-Cerro Grande Fire

Accelerated Actions


Water Canyon

(Excerpted from LA-UR-00-5359)


 


Description of Watershed

Water Canyon originates on Santa Fe National Forest lands on the eastern flanks of the Jemez Mountains. The Water Canyon watershed extends across the southern part of Los Alamos National Laboratory (the Laboratory) to the Rio Grande for a total length of about 13 mi. The watershed drains a surface area of about 6 mi2. In general the canyon floor crossing the Laboratory is relatively flat and filled with alluvium and colluvial soils eroded from the canyon walls. The canyon sides are steep and rocky with partial to full cover of trees and shrubs, particularly on north-facing slopes.

Before the fire only limited sampling was carried out in Water Canyon. To date, the Laboratory's Environmental Restoration Project has not collected samples from the canyon itself, although monitoring wells have been or will be installed as part of the groundwater management and protection program. After the fire, samples of sediments, surface water, and groundwater were collected to establish a baseline prior to any potential flood events.

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Sources and Types of Contamination

Within the Laboratory, Water Canyon passes through or adjacent to TAs-11, -15, -16, -36, -37, -68, and -71. Although no sources of contamination originate within Water Canyon itself, contaminants are known to have been transported from mesa-top TAs through discharges and surface erosion. The predominant mechanisms that influence transport within the canyon include sediment transport, dissolution/desorption, and infiltration. Most contaminants released into the canyon were retained in sediments deposited in geomorphic locations in the active and inactive channels and floodplains. These contaminants will remain in place for varying time periods, depending on their locations and surface water flow patterns. Sediment transport decreases the contaminant concentrations as the canyon extends downstream. Laboratory environmental surveillance reports show that contaminant concentrations from samples collected at the point where State Highway 4 crosses Water Canyon are not elevated.

Current knowledge of contaminants in Water Canyon is limited. Possible contaminants include those associated with high explosives (HEs) and firing-site residues, such as barium, lead and other metals, and TNT and other HEs. Most major drainage potential release sites (PRSs) at TA-16 that enter Water Canyon were characterized during investigation activities and none of these is highly contaminated. These PRSs include 16-029(g) (the TA-16-450 drainage), 16-030(h) (the TA-16-430 drainage), 16-003(a) (the TA-16-410 drainage), and 16-030(g) (the TA-16-380 drainage). None of these PRSs is a major source of contamination for Water Canyon. Very few PRSs drain directly into Water Canyon. Cañon de Valle, a tributary of Water Canyon, has significant concentrations of barium and HEs; but these concentrations attenuate to within background levels before the confluence with Water Canyon. Analysis of two samples collected in 1998 at the confluence of Water Canyon and Cañon de Valle shows no organic compounds detected and no inorganic compounds above background levels. Because Cañon de Valle has a relatively low potential for flooding, significant mobilization of contaminated sediments into Water Canyon is less likely. Waters in Martin Spring, which drains into Martin Spring Canyon and then into Water Canyon, are HE-contaminated. However, based on analyses of samples collected downgradient from the spring, little contaminant mobilization in Martin Spring Canyon has occurred.

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Impacts of the Cerro Grande Fire/Mitigation Activities

About half the total length of Water Canyon was burned by the fire, from the upper watershed to Technical Area (TA) 49. The severely burned area was confined to the upper part of the watershed west of State Highway 501, while the remainder of the watershed had only low to moderate burn severity.

Within the watershed, eight PRSs were affected by the Cerro Grande fire. Best management practices (BMPs) for erosion control have been implemented at all fire-impacted PRSs. BMPs are activities designed to prevent or inhibit contamination from reaching the canyon or migrating down the canyon and included straw bales, mulch, wattles, and wellhead protection. As a result of these mitigation activities, the potential for contaminant migration into the canyon has been reduced or eliminated.

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