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Phytotechnology Project Profiles

Phytoremediation at Boston Mill in Arizona
Last Updated: November 2007
Site Information                                                      
Site Name, Location:   Boston Mill, Fairbank, AZ, United States
Site Type:   Metal Ore Mining and Smelting
Is this a Federal
Superfund Site?
  No
Is this a Federal or
Military Site?
  No


Project Information                                                      
Project Name:   Phytoremediation at Boston Mill in Arizona
Site History and Background:   Neutral Au/Ag mine tailings from a gold and silver ore processing operation from 1879 to 1887. Located next to the San Pedro River in the San Pedro River National Conservation Area (SPRNCA), approximately 3.2 km (2 miles) south of Fairbank, AZ, and 12.6 km (8 miles) southwest of Tombstone, AZ. pH ranges from 8.3 – 9.8, Heterotrophic counts averaged 2.1 ± 0.9 × 105 CFU g−1 dry soil, autotrophic counts not determined. An initial field was performed (2003-2004) to determine 1) whether the site could be revegetated with native transplants, 2) whether compost amendment was necessary for revegetation, 3) what the impact of revegetation was on the microbial community.
Scale:   Pilot/Field Demonstration
Project Status:   Ongoing
Project Start Date:   2006
Project Completion Date:   2009
Media Treated:  
Media Qty. Geology Comments
Ground Water pH ranges from 9.3 to 9.8; Heterotrophic counts averaged 2.1 ± 0.9 × 105 CFU g−1 dry soil
Contaminants Treated:  
Contaminant Initial
Concentration
Depth Media Comments
Not specified Ground Water
Arsenic 900 mg/Kg Ground Water
Cadmium 100 mg/Kg Ground Water
Copper 3,600 mg/Kg Ground Water
Lead 16,000 mg/Kg Ground Water
Mercury 600 mg/Kg Ground Water
Zinc 8,100 mg/Kg Ground Water
Phytotechnology Mechanism(s):   Phytostabilization
Plants and other Vegetation Used:   Saltgrass
Quailbush
Saltbush
Sacaton
Planting Description:   The site was bulldozed onto a 1.5 acre impoundment and covered with 6 inches of top soil recovered locally. The site was then seeded, just prior to the summer monsoon, with the native species shown above.
Planting Area:   1.5 acres
Performance Data:   Shortly following seeding in June 2006, a large rain event washed seeds away on northern ½ of the site. Following the rain event, only four-wing saltbush and inland saltgrass were observed to have germinated, along with some volunteer species, on the southern half of the site. Sheet erosion and surface mining of the impoundment (mostly on the northern half) was noted, as well as crusting of the surface on the northern half of the site. By three months after planting (Oct. 2006), significantly more of the planted species had germinated. Four-wing saltbush, quailbush, and inland salt grass were all noted with inland salt grass the most prevalent of the seeded species. In May 2007, the total canopy cover from the seeded species for the site was 3% (± 7) on the northern half, and 16% (± 9) on the southern half. Inland salt grass was the predominant species of the overall canopy composition. A second seeding was performed in July 2007 on the northern half of the area at a higher seeding rate and will be monitored for the next few years.
Cost of the Phytotechnology Project:   Not available
Comments:   The site is being evaluated for germination and % canopy cover.

Point(s) of Contact                                                                      
    Raina Maier
Arizona University
United States
Telephone: (520) 621-7231
E-mail: rmaier@Ag.arizona.edu

Information Source(s):   Rosario, K.; S.L. Iverson; D.A. Henderson; S. Chartrand; C. McKeon; E.P. Glenn; and R.M. Maier. 2007. Bacterial community changes during plant establishment at the San Pedro River mine tailings site. Journal of Environmental Quality. (accepted)

 

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