CONCERNS ABOUT THE DOA STATE ARCHIVE FACILITY, 202 S. Thornton/201 S. Dickinson, Madison, WI, DEMOLITION AND CONSTRUCTION: Reasons for Testing DOA Building before Demolition, Apprehension about Fugitive Dust and Water Management From letter to Neil Carney, Ayres Associates Written by Maria Powell, Phd, president Midwest Environmental Justice Organization (MEJO) Community-Based Participatory Researcher Madison, 53704 mariapowell@mejo.us This summary prepared by: Diane Michalski Turner, PhD 303 S. Dickinson St, #1 Madison, WI 53703 dmturner643@gmail.com 608.294.9048 (c) 608.957.6465 608‑240-1485 Summary 1. The Environmental Assessment done by Ayres Associates (2013) for the DOA does not mention tetrachloroethylene (PCE) in the soils and groundwater of the DOA property. 2. More testing needed to understand extent of PCB contamination of soils, groundwater throughout site, and building materials. 3. Inadequate/unclear plans for preventing human exposures to toxic dust during demolition and construction. 4. Inadequate/unclear plans for controlling sediment and other runoff to Yahara River and Lake Monona during demolition and construction. 5. Inadequae/unclear plans for storm water management for the new facility. Details 1. The Environmental Assessment done by Ayres Associates (2013) for the DOA does not mention tetrachloroethylene (PCE) in the soils and groundwater of the DOA property. Concern: PCE exposure is associated with various cancers and neurological problems for all ages and with birth defects for children exposed through their prenatal development. http://www.atsdr.cdc.gov/sites/lejeune/tce_pce.html What is known: Because large metal parts, e.g., gun barrels for navy ships, were produced in the building, large amounts of solvents – PCE and TCE - may have been used (1995 Limited Phase I Environmental Site Assessment) 2006 PCB and TCE (Trichloroethylene [TCE] is a volatile organic chemical (VOC) used primarily as an industrial solvent) over Preventive Action Levels were found in the center courtyard. PCE and TCE were found in shallow groundwater far from the courtyard indicating that PCE had spread in shallow groundwater to other parts of the site. In 2010 the DNR closed the site despite the fact that only limited shallow soil and groundwater tests were done and most other areas, including areas with high potential to have PCE contamination were never tested. In 2013, from available reports: 1) no groundwater tests for PCE and other VOCs were done. 2) the few soil VOC tests did not include areas cited above that had PCE contamination 3) areas likely to have PCE contamination based on past uses, i.e., machine shops, were not tested What this means: There can be a significant PCE plume of groundwater under the site, usually only 8 – 10 feet from the surface. The plume and its depth make for a potential for vapor intrusion at this site, for nearby residents, and for those who will occupy construction over the demolished site. 2. More testing needed to understand extent of PCB contamination of soils, groundwater throughout site, and building materials. Concern: PCBs (Polychlorinated biphenyls) Toxic effects such as endocrine disruption and neurotoxicity are also associated with other compounds within the group. http://www.epa.gov/wastes/hazard/tsd/pcbs/index.htm What is known: Given previous industrial processes in the building, quantities of PCBs could have been considerable. Ayres’s Environmental Assessment I does not mention PCBs. Environmental Assessment II notes PCBs detected in the past, for this assessment no PCBs were detected in soil on the site, with the exception of GP—2 from 5 – 7 feet down. Four borings for 2013 Environmental Assessment in one small section of the site are too few to understand the extent of the PCB contamination of the block-long structure Total PCBs were found to exceed the RCL for protection of groundwater. Sources and pathways of PCBs, such as storm and sewer routes were not considered What this means: Possible PCBs found in building materials, but these have not been tested. Critical to test building materials because Environmental Assessment states some building materials will be ground on site to be utilized as fill in the new construction. 3. Inadequate/unclear plans for preventing human exposures to fugitive toxic dust during demolition and construction. Concern: Demolition and construction will go on over two years disrupting soils, groundwater, and building materials containing PAHs, lead and other metals, PCBs, PCE, and other contaminants. What is known: The Environmental Assessment does not describe how people living in the area will be prevented from exposures for this long time. What this means: Contaminants in soils and buildings need to be identified properly in order to apply proper demolition plans that fully control the release of fugitive dust from contaminated areas. 4. Inadequate/unclear plans for controlling sediment and other runoff to Yahara River and Lake Monona during demolition and construction. Concern: Contaminants from this site already have gone into the Yahara River and Lake Monona for decades. What is known: Site consultant reports from the 1990s note that sewer lines from the courtyard that was heavily contaminated with PCB and PCE ran to former the UST area and then directly discharged into the Yahara River. Existing standards allow 5 tons of sediment per acre to leave sites; this site is 5 acres. The Environmental Assessment says that the “site [will be] manipulated . . .to facilitate storm water drainage.” What this means: Storm water will be routed to drain quickly into the Yahara River. Possibility of contaminated soils and debris entering the Yahara River exists. State-of-the-art controls of run-off should be used because of the probability of contaminants on the site. PCBs, PCEs, etc. should be identified to prevent those contaminating building materials and soils from entering the Yahara River and then Lake Monona through sediment and other runoff. 5. Inadequae/unclear plans for storm water management for the new facility. Concern: Storm water system will be routed to route runoff quickly and into the Yahara River. What is known: Roof drain and storm system will be routed through a storm water management system via stormwater catch basins and underground detention storage facilities before entering the City of Madison storm sewer system that is directed north to the Yahara River. What this means: Contaminants emitted via air and other pipes and processes could enter storm water routed to the Yahara River and Lake Monona. Contaminants potentially emitted from the new facility should be anticipated along with plans for preventing their release into soils, air, groundwater, and surface water around the site.