Emerging Contaminants


Status of ECOS/DOD National Dialogue on Emerging Contaminants
Gary S. Moran, Massachusetts Department of Environmental Protection, Southeast Region

Tungsten: Emerging Heavy Metal
Mark J. Begley, Massachusetts Environmental Management Commission, Camp Edwards, MA

Overview of Perfluorooctanoic Acid (PFOA)
Brooke Moore, ENSR Corporation, Westford, MA  

Biodegradation and Bioremediation of N-Nitrosodimethylamine (NDMA) in Groundwater
Paul B. Hatzinger, Ph.D,  Shaw Environmental, Inc., Lawrenceville, NJ 

 

Status of the Environmental Council of States/Department of Defense National Dialogue on Emerging Contaminants

Gary S. Moran, Massachusetts Department of Environmental Protection, 20 Riverside Drive, Lakeville, Massachusetts, 02347, Tel: 508-946-2712, Fax: 508-947-6557, Email: gary.moran@state.ma.us.

Each of the 50 states and every U.S. territory is home to at least one military facility of some kind.  While the sustainability of the environment at these ranges is a shared goal and interest of states and the Department of Defense (DOD), there are also great pressures stemming from conflicting uses, mission, and priorities.

In 2004, recognizing the significant challenges and tensions arising between important military activities on DOD installations and need to ensure environmental protection, the Environmental Council of States (ECOS)— a national non-profit, non-partisan association of state and territorial environmental agency leaders, working with DOD, established the ECOS-DOD Sustainability Workgroup. This Workgroup serves as a focal point for discussions between ECOS and DOD regarding issues related to sustainability, and to foster cooperation and coordination in better planning and environmental management.

The Workgroup was divided into 3 major Task Groups, including the Emerging Contaminants in Groundwater Task Group.  In recent years, one of the most challenging issues confronting states and DOD has been the response to and management of emerging contaminants.  The recent experience with perchlorate illustrates some of the difficult issues surrounding emerging contaminants.

The Emerging Contaminants Task Group was formed to define the issues and challenges posed by emerging contaminants, and to develop plans of action to address such challenges.  In November 2005, the Task Group organized a forum involving state and federal stakeholders to identify and prioritize proposed actions.  Based on the Forum’s recommendations, the Task Group is currently working on the highest priority actions, including a survey of states on emerging contaminants and papers on the following issues related to emerging contaminants:
risk communication;
pollution prevention strategy and workplan;
use of provisional values in risk assessment; and
initiation of actions and funding for emerging contaminants.

Tungsten: Emerging Heavy Metal

Mark J. Begley, Executive Director, Massachusetts Environmental Management Commission, Camp Edwards, MA 02542, Tel: 508-968-5127, Email: Mark.Begley@state.ma.us

The search for alternatives to lead ammunition for small arms and to depleted uranium penetrators has been a challenge for the military and the ammunition industry.  Care must be taken that the environmental fate and transport of alternative materials, as well as the human health consequences are adequately examined and communicated to users before the material becomes widely distributed.  Based on solid science and risk assessment principles, best management practices for ranges and pollution prevention techniques covering manufacturing, deployment, use and demilitarization must be developed along with the projectiles.  The recent experience with tungsten at the Massachusetts Military Reservation is examined to demonstrate some of the information needed to make knowledgeable decisions regarding the use of alternative materials that are also emerging contaminates.

Overview of Perfluorooctanoic Acid (PFOA)

Brooke Moore, E.I.T., ENSR Corporation, 2 Technology Park Drive, Westford, MA 01886. Tel. 978-589-3000, FAX 978-589-3705, E-mail: bmoore@ensr.aecom.com
Cynthia Cogan, P.E., ENSR Corporation, 2 Technology Park Drive, Westford, MA 01886. Tel. 978-589-3000, FAX 978-589-3705, E-mail: ccogan@ensr.aecom.com
Arthur Taddeo, ENSR Corporation, 2 Technology Park Drive, Westford, MA 01886. Tel. 978-589-3000, FAX 978-589-3705, E-mail: ataddeo@ensr.aecom.com

The US Environmental Protection Agency (EPA) has been reviewing data and developing a draft risk assessment for Perfluorooctanoic Acid (PFOA).  PFOA is a synthetic chemical, sometimes referred to as “C8”, used by chemical companies and manufacturers to make non-stick cookware (including Teflon®), water repellant coatings for all-weather clothing and fabrics, food packing, gaskets, O-rings, and hoses. It is chiefly used in producing fluoropolymers which are employed in almost all commercial industry segments including aerospace, automotive, building/construction, chemical processing, electrical and electronics, semiconductor, and textile industries.  The durability of PFOA due to its specific chemical structure prevents breakdown in the environment.  This leads to widespread bioaccumulation in the food chains.  It is this bioaccumulation which prompted the EPA to conduct a further evaluation of PFOA and its potential to adversely affect human health.  Scientists do not yet know how PFOA is transported within the environment; however, studies in adult rats show that the ammonium salt of PFOA is absorbed following ingestion, inhalation, and dermal exposure.

This presentation presents a brief overview of the chemical and discusses toxicological research results, the EPA’s current status on developing a risk assessment, and the future of PFOA going forward.  

Biodegradation and Bioremediation of N-Nitrosodimethylamine (NDMA) in Groundwater 

Paul B. Hatzinger, Ph.D,  Shaw Environmental, Inc., 17 Princess Road, Lawrenceville, NJ  08648,  Tel: 609-895-5356, Fax: 609-895-1858, Email: paul.hatzinger@shawgrp.com
Sheryl Streger, 
Shaw Environmental, Inc., 17 Princess Road, Lawrenceville, NJ  08648,  Tel: 609-895-5374, Fax: 609-895-1858, Email: sheryl.streger@shawgrp.com
Jalal Hawari, Ph.D., Biotechnology Research Institute, NRC 6100 Royalmount Ave., Montreal (PQ), Canada, H4P 2R2, Tel: 514-496-6267, Fax: 514-496-6265, Email:
Jalal.Hawari@cnrc-nrc.gc.ca
Diane Fournier, Ph.D., Biotechnology Research Institute, NRC 6100 Royalmount Ave., Montreal (PQ), Canada, H4P 2R2, Tel: 514-496-6267, Fax: 514-496-6265, Email: Diane.Fournier@cnrc-nrc.gc.ca 

N-Nitrosodimethylamine (NDMA) is a potent carcinogen and an emerging groundwater contaminant in the U.S.  The objective of this research was to study NDMA biodegradation and to explore in situ and ex situ bioremediation strategies for this contaminant.  Initial studies revealed that specific propanotrophs and toluene-oxidizing strains were capable of degrading NDMA.  Two different biodegradation pathways were observed.  The toluene-oxidizer Pseudomonas mendocina KR1 initially added a single oxygen molecule to the nitroso group of NDMA to form N-nitrodimethylamine, which was subsequently metabolized to N-nitromethylamine and trace amounts of formaldehyde.   In contrast, the propanotroph Rhodococcus ruber ENV425 degraded NDMA into formaldehyde, methylamine, nitrate, nitrite, carbon dioxide, and methanol. Both degradation pathways will be presented.  To evaluate the potential for ex situ treatment, a suspended growth reactor was seeded with P. mendocina KR1 and continuously fed toluene as a primary growth substrate.   NDMA was fed to the reactor at concentrations ranging from 25 to 250 mg/L to represent typical groundwater levels.  Strain KR1 consistently removed greater than 99.9 % of the added NDMA, and effluent  concentrations below 0.09 mg/L (the MDL for the experiment) were achieved during the 4-month study.   In addition to bioreactor studies, the potential for in situ treatment of NDMA was examined using aquifer samples from three locations around the U. S.  Microcosm data indicated that indigenous bacteria capable of mineralizing 14C-NDMA to 14CO2 under aerobic conditions are indigenous in some aquifers.  However, the biodegradation process appears to be largely co-metabolic and dependent on the presence of one or more additional carbon and energy sources.  NDMA mineralization was also observed under sulfate-reducing conditions but not under denitrifying, iron-reducing or methanogenic conditions in one set of aquifer samples. The results from this research provide a basis for the further development of in situ and ex situ biological approaches for NDMA treatment.

Top
   

Past Conference Programs | Home
  
 
  
Design and Hosting by Dot.Inc Group
Copyright © 2000 University of Massachusetts - All rights reserved.