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CRISIS is the toxic waste cleanup advocacy group of Bridgewater Township, New Jersey. CRISIS has been providing critical and technical oversight on behalf of the public (regarding the American Cyanamid/Pfizer Superfund site) since 1992.


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AUGUST TECHNICAL REPORT

AMERICAN CYANAMID SUPERFUND SITE

 

CRISIS, Inc.

Ira L. Whitman, P.E., PhD Technical Advisor

 

August 2013

Issued September 20, 2013

 

 

          CRISIS reviews status reports issued to EPA by Pfizer on a monthly basis.  The August reports indicated that work on the Site-Wide Remedial Design (OU4) and the Impoundments 1 and 2 Focused Feasibility Study (OU8) is continuing.  I have reported on the details of some of this work in previous Technical Reports, and will do so again in the future.  Activities of note include:

 

·       EPA is planning a public availability meeting on the evening of October 24th to discuss the upcoming field pilot test at Impoundment 2 to begin in November.  CRISIS, Inc. plans to provide additional information on its website regarding this meeting, such as time and location, when these become known.

·       On September 19th, Pfizer and EPA met with community emergency management officials to inform them about the field pilot tests that will begin in November.  CRISIS, Inc. will report on the outcome of this meeting.

·       CRISIS will present a fact sheet of Frequently Asked Questions (FAQs) about the Impoundment 2 field pilot test on its website.

·       CRISIS, Inc. has requested that Pfizer provide our group with progress updates on key elements of the design of the OU4 site-wide remediation.  Meetings to provide these updates are to be scheduled.  CRISIS, Inc. has reiterated its concerns expressed previously to Pfizer and EPA about the site-wide remedy.

 

          For this month, I have decided to concentrate on one particular issue that underlies much of the present and future activity associated with cleaning up this site:  GROUND WATER.

 

 

1.0       GROUND WATER AT AMERICAN CYANAMID SITE

 

          Ground water is generally a misunderstood element of the natural environment that is a factor in most environmental cleanup situations, including remediation of the American Cyanamid Superfund site.

 

          Ground water is present in most locations beneath the Earth’s surface at an elevation known as the “water table.”  It is an important component of the hydrologic cycle that transfers water from precipitation through the ground to rivers and streams and ultimately to the oceans, from which it is evaporated back to the atmosphere to repeat the cycle.  Ground water supports some of the Earth’s vegetation, balances flow of water into and out of rivers, and is utilized heavily in New Jersey to provide safe potable water to millions of persons.  Ground water is a fragile ecological resource that is easily damaged in quality and diminished in quality.

 

          At the American Cyanamid site, ground water is present in two zones beneath the surface:

 

               ·          Overburden Zone – Present in the soil cover beneath the surface, as near to the surface as 5 feet at some locations, including the flood plain adjacent to the Raritan River.

               ·          Bedrock Zone – Present in cracks and crevasses in the massive bedrock beneath the site that is known geologically as the Passaic Formation.

 

          Many persons refer to ground water as “underground rivers” a concept that may describe its large presence but which does not reflect its movement.

         

          The forces of gravity cause water in the ground to move – usually very slowly in the order of several feet per year.  Dissolved contaminants in ground water move with it, but usually at a slower rate as their movement may be retarded by the soil.  At many locations, shallow ground water may move in one direction, usually reflecting local topography, while deeper bedrock ground water may move in a completely different direction at a different rate of movement (velocity).

 

 

2.0       GROUND WATER REMEDIATION

 

          At many Superfund sites, ground water cleanup is the most costly and time consuming element of the entire program of remediation.

 

          According to EPA (Removal Action Order of 2011):

 

A partial ground water containment system (at American Cyanamid) was constructed and continues operating on the Site.  The system consists of two extraction wells installed into the bedrock.  The groundwater extraction well system has been operating for approximately 30 years to control the migration of contaminated groundwater through continuous pumping. This system operates 24 hours a day seven days a week and pumps a minimum of 650,000 gallons of groundwater per day that is subsequently treated offsite at the neighboring SRVSA municipal wastewater treatment system.

 

         The system described by EPA was not designed to clean up ground water at American Cyanamid but was installed to “contain” the water and prevent contaminants from migrating off-site by exercising “hydraulic control” over the water.

 

         EPA’s Record of Decision (ROD) for Operable Unit 4 (OU4) of the American Cyanamid site was issued in September 2012, and deals with the entire site with the exception of the area on the southern portion of the site with Impoundments 1 and 2, which is known as OU8.

 

         The 2012 ROD specifies the selected (by EPA) remedy, which for ground water includes:

 

               ·          Relocation of primary bedrock extraction wells to a more central location, and adding new extraction wells.

               ·          Construction of an overburden ground water recovery system such as trenches, containment walls and shallow wells.

               ·          Treatment of ground water on-site with discharge of the treated water to surface water (Raritan River).

 

         In response to the ROD, Pfizer has been conducting geophysical testing in the bedrock to better characterize the presence and movement of the bedrock ground water, as a prerequisite to installing new wells.  The company is also in the process of completing a pilot study and laboratory testing to determine which treatment processes are likely to be needed in order to meet the requirements of the ROD to “restore the overburden and bedrock aquifers within the area of attainment to their expected beneficial use and to concentrations below the more stringent federal and state ground water quality standards within a reasonable period.”

 

 

3.0        RARITAN RIVER SEEPS

 

         In 2006 - 2007, based upon a Remedial Investigation for ground water, it was reported that shallow ground water in the vicinity of Impoundments 1 and 2 flows from north to south toward the Raritan River.  Field investigations in 2010 identified four (4) potential ground water discharges (seeps) to the Raritan River, three (3) of which were observed to be below the river’s surface water line. The fourth seep, about 65 feet long, was observed discharging from the river bank above the water line.  On December 6, 2010, a surface water sample was taken from the river at this point, to collect as much material emanating from the seep with as little dilution from the river as possible.

 

         The laboratory analysis of the December 6, 2010 water sample from the river showed concentrations of seven contaminants in excess of New Jersey Ground Water and/or Surface Water Criteria.  Six of these were metals, with the seventh being a notable contaminant marker compound known to be present within the waste stored in Impoundments 1 and 2, Benzene.

 

         The following table shows the December 6, 2010 concentrations of the seven (7) contaminants in parts per billion, micro grams/liter, or ug/l.

 

Compound

(metals)

Concentration

in ug/l

NJ Ground Water

Criteria

NJ Surface Water

Criteria

 

 

 

 

Aluminum

20,200

200

N/A

Arsenic

5.7

3

0.017

Beryllium

6.6

1

6

Manganese

4,690

50

N/A

Nickel

123

100

500

Sodium

61,700

50,000

N/A

 

Organic

Compound

Concentration

in ug/l

NJ Ground Water

Criteria

NJ Surface Water

Criteria

 

 

 

 

Benzene

20,200

1

0.15

 

          The source of the metals in the river is unclear, with some of these metals likely originating at American Cyanamid.

 

          The source of the Benzene in the river was clear – the southern portion of American Cyanamid likely including Impoundments 1 and 2.

 

          On July, 19, 2011 EPA executed an Administrative Consent Order known as the “Removal Action Order” which labeled the ground water in the vicinity of Impoundments 1 and 2 as “conditions that constitute an actual or a threat of “release” of a hazardous substance from the facility”.  The Settlement Agreement with American Cyanamid was “necessary to protect the public health, welfare, or the environment”.

 

 

          Referring to the discharge to the Raritan River, EPA ordered American Cyanamid to

         

Design and construct a Removal System which will block, intercept and capture or otherwise address to EPA’s satisfaction (i) the known seeps… (ii) any other seeps discovered during construction of the removal system, and (iii) those seeps or discharges identified in studies … that are found discharging to the Raritan River, Cuckel’s Brook or from the Route 287 Pond to the Raritan River and Middle Brook…

 

          In 2012, Pfizer constructed a cutoff wall between Impoundments 1 and 2 and the river, and a small wastewater treatment plant for the ground water intercepted near the river.  This interception and treatment system began operating in May 2012.  Modifications to the system were developed to deal with such issues as freezing, toxicity testing of effluent and treatment plant operation.

 

         Water quality samples from the Raritan River are collected quarterly, and have been reported on in my previous Monthly Technical Reports.  Through January 2013, concentrations of Benzene in the river at three (3) locations in the vicinity of Impoundments 1 and 2 exceeded the NJDEP surface water standard of 0.15 ug/l (parts per billion).  In my June 2013 report, I reported that for the first time, in May 2013, Benzene at all locations in the river were in compliance with the 0.15 ug/l standard.

 

         CRISIS will continue to report on Raritan River surface water quality as the results of new quarterly sampling rounds are received.

 

 

4.0        CUCKEL’S BROOK SEEPS

 

         Cuckel’s Brook is a small stream that internally transects the American Cyanamid site, flowing into the Raritan River from northwest to southeast.  The natural flow of the brook is very small, but in the past it carried the effluent from the SRVSA waste treatment plant which greatly exceeded in volume the natural stream flow.  Cuckel’s Brook does carry a small volume of shallow ground water inflow to the stream from American Cyanamid at locations on the property where the shallow ground water remains highly contaminated, including the areas adjacent to Impoundment 5 and Impoundment 2.

 

          As reported in my May 2013 Technical Report, on May 6 a sheen (small oily slick) was observed on Cuckel’s Brook in the vicinity of one of the surface water sampling locations, and further observation showed the presence of a ground water seep into the brook.  The water at the location of the seep was sampled and analyzed as reported in June.  In my July report, I indicated that following inspection of the entire length of the brook running through the property, other seeps into Cuckel’s Brook were found.

 

          The following actions were reported by Pfizer as having been taken as a consequence of their findings with regard to Cuckel’s Brook.

 

·       Water samples from two of the newly discovered seeps were taken on July 24.

 

·       Preliminary data from the seeps indicated that the impact to water quality in the stream warrants an interim treatment measure; carbon bags to treat water on a temporary, localized basis.  EPA has approved this as an interim measure.

 

          CRISIS, Inc. recommends that Pfizer continue to monitor water quality in Cuckel’s Brook, and to evaluate whether the interim measures taken in response to these discharges are adequate and appropriate based on the mass of the contaminants seeping into the brook.  Pfizer should determine whether additional measures are needed to protect surface water until the long term collection and treatment measures for site-wide ground water issues prescribed in EPA’s 2012 ROD are implemented.

 

          Ground and surface water will continue to be a major concern to CRISIS, Inc.  We anticipate the need to report frequently on ground water issues at the American Cyanamid site.

 

 

 

 

                                                                                    Ira L. Whitman, P.E., Ph.D.

                                                                                    Technical Advisor to CRISIS, Inc.

                                                                                    September 20, 2013




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MONTHLY TECHNICAL REPORT

AMERICAN CYANAMID SUPERFUND SITE


CRISIS, Inc.

Ira L. Whitman, P.E., PhD Technical Advisor


July 2013

Issued August 16, 2013



  1. impoundments 1 and 2 (OU8) Update


CRISIS met with Pfizer and EPA on July 23 to review progress on the Impoundments 1 & 2 Pilot Test Program phase of the OU8 Focused Feasibility Study.


Impoundments 1 & 2 cover a total area of nearly 4 acres on the south side of the American Cyanamid site.  They are located approximately 800 feet north of the Raritan River, in the flood plain.  For over 50 years they have contained solid and semi-solid waste from a coal light-oil refining process, with three distinct layers of waste; a light-oily sludge, a viscous-rubbery tar layer, and a hard-crumbly tar layer.  The material is difficult and nasty to handle as a consequence of its physical properties and chemical properties.  It is highly acidic, with sulfuric acid being used in the industrial operations that produced the waste.


The waste material to be treated contains Volatile Organic Compounds (VOC) including benzene derivatives, and Semi Volatiles including Napathlaene.  The waste material gives off strong odors, and vapors.  The pilot test will be conducted in Impoundment 2. 


In November 2012, Pfizer briefed CRISIS on its EPA-approved plan to determine the best methods for treating these wastes by performing large scale pilot studies in 2013, which follow bench scale laboratory treatability studies conducted in 2012.  Pfizer’s report to CRISIS on July 23, 2013 detailed the concept and design for the pilot studies. 


Key elements of Pfizer’s report to CRISIS include Pilot System Construction, August-November 2013; and Pilot Study Operations, November 2013 -March 2014.


Construction steps will include:


  • Infrastructure for the test, Aug/Sept, including construction of a test area bench, flexi floats and anchoring.
  • Conduct a clay tar survey, September
  • Installation of caissons within which pilot test will be performed, October 
  • Vapor treatment system construction and start-up, November


Berm Armoring:


  • Sept. 2013, Pfizer will reinforce the berms surrounding Impoundments 1 & 2 for containment


Pilot Study Operations:


  • Thermal treatment, Nov 2013 - Feb 2014
  • Stabilization/Solidification, Feb/Mar 2014


The pilot study infrastructure and berm armoring are designed to withstand flooding from The Raritan River should that occur between now and March 2014.


Three treatment processes will be undertaken during the November-March testing period:


  1. Thermal treatment of the waste
  2. Stabilization and solidification
  3. Combination of 1 & 2


In addition, vapors released by the thermal treatment will be collected and treated.


Safety elements incorporated into the design include:


  • Ability to withstand category 2 hurricane events
  • Vapor treatment system elevated above the flood plan
  • Thermal treatment will be conducted under oxygen-deprived conditions
  • All processes were evaluated using a Process Hazard Assessment.


Pfizer is installing piezometer wells around the periphery of Impoundment 2 to monitor ground water quality before, during and after the pilot test.


During the pilot test, real-time air quality monitoring will be conducted at locations along the perimeter of the American Cyanamid property. If the air quality test results are unsatisfactory, or if there are unacceptable odors, the test will be shut down.


Following the pilot test, EPA and Pfizer will evaluate the results to determine which methods are most effective and feasible in remediating the hazardous chemicals stored in Impoundments 1 and 2. 


As the test moves forward, CRISIS will provide updates to the community as we follow the pilot study program in detail.  As the results of the pilot testing are factored in to the overall Feasibility Study for Impoundments 1 and 2, CRISIS will focus its attention on the critical ultimate question for this area of the site: Can the treated waste material be allowed to remain in place in an area where Impoundments 1 and 2 are capped, or will the waste have to be removed following full treatment with permanent disposal off site in a secure landfill?


  1. site-wide remedial design (ou4)


EPA has designated Operating Unit 4 (OU4) as all areas of the American Cyanamid site for soil and ground water excepting Impoundments 1 & 2.  Pfizer’s schedule for OU4 calls for submittal of the 30% design for the site-wide ground water treatment facility to EPA in September 2013.


While interim removal and treatment measures for ground water control and treatment are presently in operation, the ultimate plan for ground water remediation is to collect ground water from shallow and deep bedrock wells site-wide, and to treat ground water at one on-site facility, equipped with several treatment processes.  The effluent from the site-wide facility is to be discharged into the Raritan River, an event which his several years in the future.


Pfizer has been conducting laboratory testing on ground water, and pilot studies on various proposed treatment processes for the site-wide ground water remediation.  The treatment processes selected will have to be capable of removing volatile organics, semi volatile organic compound and metals. 



  1. cuckel’s brook


In my May and June 2013 Technical Reports I discussed the finding of a contaminated ground water seep into Cuckel’s Brook, on the American Cyanamid site.  This seep is located in the vicinity of the highly contaminated Impoundment 5.


Pfizer reports that the entire American Cyanamid site is bounded by fencing to keep unauthorized persons from entering, and that there are physical barriers on the brook itself that will prevent persons from exposure to the brook and the contaminated seeps. 


Following inspection of the entire length of the brook, other seeps have been found.  Pfizer is submitting a work plan to EPA for interim measures to contain and intercept these seeps, to keep the contaminants from reaching Cuckel’s Brook.


The newly discovered seeps were to be sampled later in July.  CRISIS will be given the sampling results and I will discuss the results in a subsequent report.  The seeps impact water quality in Cuckel’s Brook adversely, but due to the small volume of water seeping into the Brook, the total volume of contaminates impacting the brook is relatively small. 


The source of the seeps is chemicals in the ground water derived from waste discharges or storage in the immediate vicinity of the brook, indicating that shallow ground water in these areas is not fully under control.  Eventually this ground water will be collected and treated at the site-wide ground water treatment facility under design as discussed under Site-Wide Remedial Design, Section 2.0 of this report. 


CRISIS will continue to monitor Pfizer’s findings and actions with regards to Cuckel’s Brook.  



Ira L. Whitman, P.E., Ph.D.

Technical Advisor to CRISIS, Inc.

August 15, 2013

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MONTHLY TECHNICAL REPORT

AMERICAN CYANAMID SUPERFUND SITE

 

CRISIS Inc.

Ira L. Whitman, P.E., PhD Technical Advisor

 

June 2013

 

 

          EPA’s monthly status update meeting with CRISIS, Inc. was held on June 24, 2013.  Ross Stander and Dr. Ira Whitman participated on behalf of CRISIS, Inc.  The format for the monthly call has been changed by Pfizer who is now providing EPA with monthly progress reports as required under the recent Administrative Settlement and Order of Consent executed between Pfizer and USEPA.

 

 

1.0        surface water sampling results

 

          Pfizer conducted surface water sampling in early May at 10 locations in the Raritan River, 9 locations in Cuckels Brook (which transects the American Cyanamid Property), and at one location in the Millstone River and one in Middle Brook.

 

          Of primary interest, concentrations of benzene in the Raritan River diminished in May 2013 relative to all previous sampling events.  In the three sampling locations of greatest concern, immediately downstream of Cuckel’s Brook, the benzene concentration changes from January to May 2013 were as follows.

 

 

 

Benzene- ug/l*

 

Sampling Location

Approximate Distance below entry point of Cuckel’s Brook

 

January 2013

 

May 2013

RR-05

650’

0.8

0.13

RR-04

1125’

0.37

0.11

RR-03

1650’

0.22

Below detection

 

*ug/l- Micrograms per liter

 

          Notably; the NJDEP surface water quality criteria for benzene is 0.15 ug/l, so for the first time, in May 2013 all surface water samples from the Raritan River met this standard for benzene.

 

          In Cuckel’s Brook, as before, benzene was detected in seven surface water samples, CB-02 through CB-08, a distance about 0.8 miles.  This stretch of Cuckel’s Brook is directly adjacent to much of the waste storage and disposal areas of the American Cyanamid site.  While concentrations of benzene and other organic compounds exceed standards in Cuckel’s Brook, the volume of flow in the brook is quite small, hence the net contribution of organic contaminants to the Raritan River from Cuckel’s Brook is low.

 

 

2.0       ground water seep into cuckel’s brook

 

In my May 2012 Technical Report, I reported the presence of a small seep of ground water into Cuckel’s Brook near samplings station CB-06.  Pfizer has provided the analytical data from a sample taken of the seep to CRISIS, and as would be expected there are very high concentrations of a number of organic compounds.  The compounds listed below are present in the seep in concentrations that exceed the concentrations of the same chemicals nearby at CB-06 in Cuckel’s Brook by at least 3 orders of magnitude (1000x)

 

 

1,2 Dichlorbenzene

1,2 Dichloroethene

Acetone

Benzene

Chlorobenzene

Xylenes

Toluene

Anilene

 

          As a result of finding this ground water seep, Pfizer and USEPA conducted an inspection of much of the length of Cuckel’s Brook and identified other locations with ground water seeping into the brook.  These other discharges are to be sampled on July 17. 

 

          Pfizer may pursue an interim treatment action for the contaminants finding their way into the brook, utilizing activated carbon bags along the bank of the brook.  Ultimately Pfizer will have to intercept the seepage flow into the brook, collect it and treat it, likely as part of its site-wide ground water collection and treatment program, which is presently in the design phase (Operating Unit-OU4)

 

          CRISIS will continue to follow this relatively new development at the American Cyanamid site, and periodic updates of how this is being managed will be presented in future Monthly Technical Reports.

 

 

3.0        Pfizer status update

 

          Pfizer’s work on designing its Pilot Study for Impoundments 1 & 2 is progressing on it’s revised schedule.  Construction related to the pilot study is scheduled to begin in late July, and the pilot study itself is scheduled to begin in late November 2013 at The American Cyanamid site.

         

          Pfizer is looking to accelerate its treatment of water contained in an impoundment known as Lagoon #7, which primarily contains storm water.  Following treatment for pH adjustment using neutralization and filtration, the water in Lagoon #7 will be discharged into the sewerage system operated by the Somerset Raritan Valley Sewerage Authority.


 

 

          CRISIS is scheduled to meet with Pfizer and EPA on July 23 to review progress on the Impoundments 1 & 2 Focused Feasibility Study (OU8).  We will report on the results of this meeting in the next Technical Advisors Report.

 

 

 

                                                                                    Ira L. Whitman, P.E., Ph.D.

                                                                                    Technical Advisor to CRISIS, Inc.

                                                                                    July 15, 2013

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MONTHLY TECHNICAL REPORT - MAY 2013 
AMERICAN CYANAMID SUPERFUND SITE

CRISIS Inc.
Ira L. Whitman, P.E., PhD Technical Advisor

May 2013


    EPA’s monthly status update meeting with CRISIS, Inc. was held on May 20, 2013.  Ross Stander and Dr. Ira Whitman participated on behalf of CRISIS, Inc.  The format for the monthly call has been changed somewhat by Pfizer who is now providing EPA with monthly progress reports as required under the recent Administrative Settlement and Order of Consent executed between Pfizer and USEPA (see my April 2013 Technical Report).  Future monthly status meeting are being changed from the third to the fourth Monday of each month.


downstream water intakes from raritan river

    CRISIS recently received an inquiry as to the presence of drinking water supply intake from the Raritan River downstream of the American Cyanamid Superfund site.  The query implied that any such intakes should be coupled with extensive analysis of any contaminants in the river water, and measures to treat such water prior to distributing it for potable use.

    Information provided by the New Jersey Water Supply Authority indicates that no drinking water supply intakes are situated on the river downstream of The American Cyanamid site.  This is both good news in terms of potential impacts to the public from the Superfund site, and logical as the Raritan flows southeastward from Bridgewater and Bound Brook.  The river becomes tidal in less than 5 miles, and once tidal is no longer suitable as a source of fresh potable water.


background on public water supply sources for bridgewater

    For a state that is one of the smallest (in geographic extent) in the nation, New Jersey has a complex system of public water supply agencies and private water companies that utilize a multitude of fresh water sources delivered to millions of residents and businesses through a complicated network of public water systems

    All public water systems1, in New Jersey and the country are required to perform, at a minimum, the following steps.

Sample and monitor water at its point of entering the system
Provide physical and chemical treatments to meet state wide drinking water standards
Provide disinfection to meet bacteriological standards
Meet taste and odor requirements based on subjective parameters in these categories
Sample finished water following treatment
Publish its finished water quality data and distribute such data to its customers

    Chris Paulson, of the Bridgewater Health Department reports that Bridgewater presently relies largely on surface water as provided by the New Jersey American Water Company, whereas 20 years ago a significant volume of water was withdrawn from the ground using wells in the Finderne section of the Township2.

    It should be understood that CRISIS, Inc. does not provide monitoring, study or evaluation of any public water systems (nor of private well) or treatment of them in any municipality or region.  This is not part of CRISIS, Inc.’s mission.

    CRISIS does seek to understand whether contamination from the American Cyanamid site enters ground water aquifers or surface water sources (e.g. Raritan River) of potable water.


Pfizer status update

    Much of the progress reported by Pfizer in its May 20 status meeting pertains to pre-determined milestones with regard to its primary remediation activities, and its interaction with the regulatory agencies, USEPA and NJDEP.  Highlights include:

    Impoundments 1&2 Focused Feasibility Study (OU 8)

EPA has provided comments to the 30% design for Impoundments 1&2 (now referred to as OU [Operating Unit] 8)
Pfizer anticipates that the field pilot study for the two impoundments will be carried out from November 2013 through March 2014.  (The actual study will be conducted in Impoundment 2).
EPA anticipates conducting a public information meeting regarding the OU 8 field pilot study several months prior to the start of the study

    Site Wide Remedy (OU4)

The ground water treatment Feasibility Pilot Study is on-going.  A comprehensive ground water plan is expected during the first half of 2014.
Pfizer is conducting a Flood Storability Analysis and planning for soil importation, the results of which will be shared with CRISIS.
Pfizer’s quarterly surface ground water and sediment monitoring program was carried out on May 6.  At that time a partial drum was found in Cuckel’s Brook, removed and laboratory analyzed.

    Impoundments 1 & 2 Ground Water Removal Action

A sheen was observed on Cuckel’s Brook and further examination led to the discovery of a ground water seep into Cuckel’s Brook in the vicinity of sampling station CB-06.  Laboratory analysis of the water from the seep indicated the presence of many volatile organic and semi volatile organic compounds, including benzene, toluene and chlorinated solvent compounds.  Since Cuckel’s Brook discharges directly into the Raritan River, CRISIS will continue to review all surface water quality results for samples taken from the Raritan River.  Pfizer was scheduled to conduct its 2nd quarter 2013 surface water and sediment sampling in the River during the second week of May.  The sampling results will be discussed by me once the analytical data are made available by Pfizer.
As a result of discovering the ground water seep, Pfizer will perform a reconnaissance of the balance of the areas adjacent to Cuckel’s Brook.
EPA and Pfizer are developing a plan for soil removal between the subsurface barrier wall and the Raritan River, designed to reduce the amount of benzene seeping into the River.


                Ira L. Whitman, P.E., Ph.D.
                Technical Advisor to CRISIS, Inc.
                June 20, 2013


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Monthly Technical Report - April 2013
American Cyanamid Superfund Site
 
 
CRISIS Inc.
Ira L. Whitman, P.E., PhD Technical Advisor
 
 
April 2013
 
          EPA's monthly status update meeting with CRISIS, Inc. was held on April 15, 2013.  Ross Stander and Dr. Ira Whitman participated on behalf of CRISIS, Inc.  One issue discussed that is of particular interest to CRISIS Inc. is Whole Effluent Toxicity Testing, conducted by Pfizer on the effluent from the ground water treatment system installed to treat ground water collected in the vicinity of Impoundments 1 and 2.
 
1.0         "WHOLE EFFLUENT TOXICITY TESTING"
 
          In my Monthly Technical Report for March 2013 I discussed how surface water in The Raritan River and Cuckel's Brook is sampled quarterly throughout the year, to determine impacts to the river from contaminated ground water in the vicinity of Impoundments 1 &2, and from the discharge of Pfizer's ground water treated system into Cuckel's Brook.  I reported that at some locations in the Raritan and Cuckel's Brook concentration of benzene exceeded New Jersey's
surface water quality standard for benzene of 0.15 parts per billion.
 
          I also reported that Pfizer believes that concentrations of benzene in surface water will decrease over time, and that CRISIS, Inc. will carefully monitor Raritan River water quality sampling data.
 
          A second type of sampling is performed on the discharge from the Pfizer ground water treatment plant, known as "Whole Effluent Toxicity Testing", which are biological tests conducted to monitor the impact of the treated effluent on one or more selected test organisms.  In the case of the American Cyanamid site, the test organisms specified were daphnia, defined as "a variety of small freshwater crustaceans of the genus Daphnia.”
 
          Some species of Daphnia are commonly used as food for aquarium fish.  Daphnia are important organisms in the freshwater food chain; therefore their reaction to treated wastewater or ground water is an important indicator as to whether a treated effluent has a deleterious impact on the aquatic ecosystem.
 
          In March 2013, Pfizer reported that it had to make several corrective actions to its ground water treatment as a result of unfavorable results from its Whole Effluent Toxicity Testing.  These changes consisted primarily in corrections to chemical imbalances due to natural ground water chemistry, and to the adjustment of the pH (acidity) of the final effluent.  In January, USEPA had approved Pfizer's Preliminary Corrective Action Plan to investigate issues with its Whole Effluent Toxicity Testing.
          In Pfizer's most recent toxicity test report dated March 27, 2013 the laboratory results indicated a 100% reproductive success rate of the test species following the chemical modifications made in the pH adjustment.  With these tests having been successful, Pfizer plans to make modifications to its ground water treatment equipment that will allow the substitution of calcium hydroxide for sodium hydroxide for pH adjustment.
 
 
2.0         SITE-WIDE GROUND WATER TREATMENT
 
          Pfizer will face similar issues in approximately two (2) years when it implements its site wide ground water treatment programs by collecting ground water from the entire American Cyanamid site, including Impoundments 1 & 2.  Presently, all ground water collected at the site except Impoundments 1 & 2 is being discharged through the publically owned facility operated by Somerset Raritan Valley Sewerage Authority.
 
          To reach the point of being able to design and construct a site-wide treatment system, Pfizer has developed a Pilot Study Work Plan to evaluate the various treatment processes that may be utilized in a site-wide system.  EPA has reviewed and commented on the Pfizer work plan and the draft plan has been revised in response to EPA's comments.
 
          The development of an effective site-wide ground water treatment system is an important milestone in implementing a site-wide remedy for American Cyanamid, and CRISIS, Inc. will be paying close attention to Pfizer's progress and to the direction that this component of the site-wide remedies takes.
 
3.0         PFIZER STATUS UPDATE
 
          Much of the progress reported by Pfizer in its April 15 status meeting pertains to pre-determined milestones with regard to its primary remediation activities, and its interaction with the regulatory agencies, USEPA and NJDEP.  Highlights include:
 
          Impoundments 1&2 Focused Feasibility Study:
 
· Permit-equivalency applications for the field pilot treatability study are to be submitted in early May.
· Pfizer and EPA met to discuss the 60% pilot treatability study design status.
 
          Impoundments 1&2 Ground Water Removal Action
 
·        Pfizer reported on the success of its modifications to ground water treatment as reflected by the Whole Effluent Toxicity Testing (see Section 1.0 of this report)
·        Soil was excavated between the subsurface cutoff wall and the Raritan River, to be landfill disposed off-site.

 
          Site-Wide Remedy
 
                 ·   An Administrative Settlement Agreement and Order of Consent for Remedial Design (OU 4 and OU 8 in accordance with the Record of Decision of September 2012). Project coordinators for the two operable units were named.
                 ·   Pfizer presented USEPA and NJDEP a revised Baseline Ground Water Monitoring Work Plan.  Pfizer's plan includes an update of recent geophysical testing at the site and pilot testing for future planned bedrock extraction wells and overburden collection trenches.
 
          Ambient Air Monitoring
 
                    ·            Ambient air sampling was conducted in early April
 
          Surface Water & Sediment Monitoring Program
 
                    ·            Sampling is scheduled for May 6-10
 
          Ground Water Monitoring Program
 
                    ·            1st half 2013 ground water sampling took place on April 1-12.
 
 
 
 
 
                                                                                    Ira L. Whitman, P.E., PhD
                                                                                    Technical Advisor to CRISIS, Inc.
                                                                                    April 30, 2013

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Monthly Technical Report - March 2013
American Cyanamid Superfund Site
 
CRISIS, Inc.
Ira L. Whitman, P.E., PhD Technical Advisor
 
 
March  2013
 
          EPA’s monthly status update meeting with CRISIS, Inc. was held on March 18, 2013.  Ross Stander and Dr. Ira Whitman participated on behalf of CRISIS, Inc.  One issue discussed that is of particular interest to CRISIS Inc. is the surface water quality sampling conducted quarterly by Pfizer.
 
 
1.0        UNDERSTANDING UNITS AND TERMINOLOGY FOR SOIL AND WATER SAMPLING RESULTS
 
          I was asked by CRISIS’ Chairman, Ross Stander to provide an explanation on the units of measurement commonly used to report the results of sampling for contaminants in soil, surface water and ground water at Superfund and other sites where remediation is conducted.
 
          It should be recognized that in most cases we are reporting very low concentrations of contaminants, and hence these concentrations are reported (but not in the actual laboratory data) in parts per million and parts per billion (Think of one blue ping pong ball in Madison Square Garden filled with white ping pong balls).
 
          1 part per million (ppm) is the equivalent of 0.00001% concentration of the contaminant, and 1 part per billion (ppb) would be 0.00000001%.
 
          By contrast, sea water contains approximately 3.5% salt, or 35,000 parts per million.
 
          However, the terms “parts per million and billion” are popular equivalents for the actual units used in laboratory reports of soil and water samples.
 
          Soil:
 
          Concentrations of contaminants in soil are reported on a weight per weight basis.
 
          for soil contaminants:
 
          1 part/million (1 ppm) = 1milligram/kilogram, 1 mg/kg
          1 part /billion (1 ppb) = 1 microgram/kilogram, 1 μg/kg
 
          Water:
 
          Concentrations of contaminants in surface water and ground water are reported on a weight per volume basis, and therefore on a very high contaminant concentration there is not an exact 1 to 1 correspondence between parts per million/billion and the actual reported unit.  However, at the low concentrations typically encountered, the equivalence is close enough for all practical purposes.
 
          for water contaminants:
 
          1 part/million (1 ppm) = 1 milligram/liter, 1 mg/l
          1 part/billion (1 ppb) = 1 microgram/liter, 1 μg/l.
 
          For purposes of my reports to CRISIS I will report results in ppm or ppb, while the lab data provided to me are in mg/l or μg/l.
 
 
2.0        SURFACE WATER QUALITY
 
          The Raritan River borders the American Cyanamid Superfund site to the south, winding from southwest of the site for 3,600 feet until the junction with the Millstone River, and then southeast of the site for approximately 8,400 feet.  The river flows west to east in the area of the site.
 
          Cuckel’s Brook (also known as Cuckhold’s Brook) disects the site and empties into the Raritan River.  Until recently, the Somerset-Raritan Valley sewage treatment plant discharged into Cuckel’s Brook, but several months ago that discharge was moved and now it discharges directly into the Raritan, in the vicinity of Impoundment 18.
 
          Pfizer’s Ground Water Removal Action instituted to divert ground water discharging benzene into the Raritan River operates by intercepting ground water with a cutoff wall and trenches, collecting the flow and treating it at a temporary treatment plant, which discharges into the lower stretch of Cuckel’s Brook near Impoundment 2.
 
          Pfizer instituted quarterly sampling of sediment and surface water in the Raritan River and Cuckel’s Brook in August 2012.  In general, contaminants from the American Cyanamid site have not been detected in the river sediments.  However, benzene, one of the principal contaminants in Impoundments 1 & 2 has been present in surface water at some locations in Cuckel’s Brook and the Raritan River, as discussed below. (As well as a few other Volatile Organic Compounds, but benzene is used as the “marker” when evaluating contamination.)
 
          The sampling laboratory results for benzene and other Volatile Organic Compounds are reported by Pfizer’s consultants in micrograms per liter (μg/l) or parts per billion (ppb).  The NJDEP Surface Water Quality Standard (for human health) for benzene is 0.15 part per billion; whereas the NJDEP Ground Water Quality and Drinking Water Standard for benzene is 1.0 part per billion.  Thus, the quality of water in the river for benzene is expected to be better than is required for potable water.
 
          Cuckel’s Brook:
 
          There are 10 surface water sampling locations on Cuckel’s Brook.
 
          Samples taken in August and October 2012 were all acceptable; i.e., below the surface water quality standard for benzene.  However, in December 2012 the SRVSA discharge was removed from Cuckel’s Brook, resulting in a significantly lower volume of water flow thereby removing the dilution flow provided by the treated sewage.
 
          Samples taken in January 2013 exceeded the benzene surface water quality standard in Cuckel’s Brook at different locations, likely attributable to inflow into the Brook from Impoundments 1 & 2 as well as several upstream areas on the American Cyanamid site.  Benzene concentrations exceeded the 0.15 part per billion standards at the following locations.

 


 
          Raritan River – Below Cuckel’s Brook:
 
          There are 5 Raritan River sampling points below (downstream) where Cuckel’s Brook empties into the river.  Three of these points are adjacent to Impoundments 1 & 2, and the ground water seeps into the river from American Cyanamid discovered in 2011; RR – 05, RR – 04 and RR – 03.  The other two points are further downstream on the other side of Interstate I-287, below where Middle Brook empties into the Raritan.
 
          Benzene has been found at these sample locations since sampling began in 2012.

 

 
          The surface water quality data for this section of the Raritan River shows clearly that benzene concentrations are highest near Cuckel’s Brook and Impoundment 2, and decrease with distance in the downstream direction.
 
          Raritan River Above Cuckel’s Brook:
 
          There are 5 Raritan River sampling points above (upstream) where Cuckel’s Brook joins the Raritan, and there is one point on the Millstone River.  All of these points are adjacent to the American Cyanamid site, these sampling points are identified as RR – 06, RR – 07, RR – 08, RR – 09, RR – 10 and MS – 01.
 
          At all 6 locations, for each of the August, October and January sampling dates, benzene concentrations were found to be not detected above the reporting limit.
 
          Conclusions on Surface Water Quality:
 
          Volatile Organic Compounds from soil, ground water and impoundments at the American Cyanamid Superfund site are having no impact on the river upstream of Cuckel’s Brook and Impoundment 2.  However, in Cuckel’s Brook and in the Raritan River for 1,400 feet below Cuckel’s Brook benzene is present above the surface water quality standard of 0.15 parts per billion, likely from two (2) sources:
 
1.        Discharges from Pfizer’s treatment plant along Cuckel’s Brook treating ground water collected from the Impoundments 1 & 2 area
2.        Seepage of ground water directly into the Raritan River from the Impoundments 1 & 2 area.
 
          Pfizer believes that concentrations of benzene in surface water will decrease over time as its ground water interception structures divert more organic contaminants from direct seepage into the river, and as it designs, constructs and operates its site-wide ground water collection and treatment facilities, scheduled to begin in 2015.
 
          CRISIS, Inc. will be monitoring Raritan River surface water quality quarterly as data is received from Pfizer, and will periodically be reporting on the results in the Technical Advisor’s Monthly Technical Report.
 
 
3.0        PFIZER STATUS UPDATE
 
          Impoundments 1 & 2 Focused Feasibility Study:
 
          Pfizer’s Focused Feasibility Study, Draft Laboratory Treatability Study Report for Impoundments 1 & 2 is presently under review by EPA’s office of Research and Development.  The results of the treatability study were presented by Pfizer and its consultant, CH2MHill at the CRISIS project update meeting on February 27.
 
          Pfizer presented EPA with its field test 30% design memo.  Pfizer will be constructing an elevated platform in the flood plain near Impoundment 2 for the placement of vapor treatment equipment for the field pilot study later this year.
 
          Impoundments 1 & 2 Ground Water Removal Action:
 
          Pfizer has modified its procedures for whole effluent toxicity testing of effluent from the ground water treatment system that went operational in May 2012, and is modifying its pH adjustment procedure from potassium to sodium hydroxide.  Ground water extraction and treatment are on-going.
 
          Concentrations of benzene have decreased in the river; however in the areas of the benzene seeps concentrations still exceed the 0.15 part per billion standard.  See Section 2.0 of this report for more detail on surface water quality.
 
          Site-Wide Remedy:
 
          USEPA and Wyeth Holdings Corporation (Pfizer) executed an Administrative Settlement Agreement and Order of Consent for Remedial Design, Operable Unit 4 (and Focused Feasibility Study, Operable Unit 8) on March 18.
 
          Geophysical studies were concluded that are expected to provide necessary data for locating future ground water extraction wells that will intercept ground water plumes within the most productive zones of fractured bedrock beneath the site to provide hydraulic control and contaminant mass removal.
 
          NJDEP had recommended a NJPDES Permit-By-Rule for a pilot ground water treatment system that will enable Pfizer to evaluate the most appropriate ground water treatment technologies for the future site-wide ground water treatment plant.
 
          Pfizer is preparing to conduct a Baseline Ground Water Monitoring Program in April.
 
          Ambient Air Monitoring Program:
 
          Reports for Fourth Quarter 2012 and First Quarter 2013 have been presented to USEPA, NJDEP and Bridgewater Township.  They are awaiting EPA approval.  Ambient air quality for these 2 quarters has been largely similar to the previous 2 quarters, except for an improvement in benzene levels  and a detection of hydrogen sulfide near Impoundment 2.
 
          Surface Water and Sediment Monitoring:
 
          First quarter surface water and sediment data were provided by Pfizer to EPA, and Pfizer received comments from EPA on its 2012 water and sediment monitoring report.
 
          NOTE:      See Sections 1.0 and 2.0  for more discussion on surface water quality in Cuckel’s Brook and the Raritan River.
 
          Ground Water Monitoring Program:
 
          Second half 2012 ground water monitoring data were presented to USEPA.
 
          Pfizer has given STS (Tires) access to its site near its boundary with STS for soil and ground water sampling on the Pfizer property.
 
 
4.0        TECHNICAL PROGRESS UPDATE MEETING, FEBRUARY 25
 
          As EPA’s TAG grant recipient for the American Cyanamid Superfund Site, CRISIS conducted a public stakeholder’s meeting on February 27 at USEPA offices in Edison, New Jersey.  The presentations at the meeting were conducted by Pfizer and its contractor CH2MHill.  Sessions were presented on these subjects and issues:
 
·       Background and history of Impoundments 1 &2
·       On-going ground water removal action
·       On-going site sampling and monitoring
·       Impoundments 1 &2 Focused Feasibility Study process.
 
          CRISIS, Inc. moderated an extensive question and answer session following the presentation.  A separate report on this meeting will be posted on the CRISIS web site.
 
 
 
                                                                                    Ira L. Whitman, P.E., PhD
                                                                                    Technical Advisor to CRISIS, Inc.
                                                                                    April 11, 2013




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CHAIRMAN’s REPORT, March, 2013
From Ross Stander, Exec. Chairman




Note:  Please also see the latest Technical Report (Feb. 2013) from our Technical Adviser, Dr. Ira Whitman. [News Articles, Technical Reports, Memoranda and so on, are arranged in chronological order below]

REMEDIATION HIGHLIGHTS

1) The Record of Decision (ROD) for OU4 (Operable Unit 4 in official parlance) was issued by US-EPA in Sept. 2012.   The OU4 ROD covers much of the Cyanamid site including Impoundments 3, 4, 5 and 13, 17 & 24 plus contaminated site soils, groundwater and related wetlands. (But it excludes Impoundments 1&2, the most difficult areas to remediate.  This ROD provides the remediation plan for OU4 as was presented in the Site-wide Feasibility Study (SWFS) at the public hearings in March 2012.  CRISIS conditionally signed off on this EPA remediation plan subject to various important conditions that would strengthen the plan in our view.  These CRISIS conditions have to do with armoring the soil caps against erosion; moving certain principal threat-materials (PTWs) to a berm-protected location on-site (within which groundwater is pumped and then treated; and providing for more flood protection devices.  Our conditions can be found on this website dating to our official response letters to EPA of last Spring, 2012.

2) Treatability Studies for Imp. 1&2 (also called OU8):
For the worst impoundments (#1&2) on site, Pfizer hired the respected consulting firm CH2MHill to analyze the high concentration benzene and other VOCs therein (both tarry and crumbly textures as it turned out), evaluate alternative remedial solutions, and perform laboratory treatability studies for leading candidates.  These studies were reported to CRISIS and others initially on Nov. 14, 2012 in an EPA sponsored meeting in Bridgewater.  Our report to members on this meeting by Dr. Whitman, our TA, is on this website under the “Impoundment 1&2” tab.  

As of February 2013, no decision has yet been made on the remediation plan that Pfizer will submit to EPA for Imps. 1&2.  The next step in this process, which is part of EPA’s Focused Feasibility Study (FFS) process for Imps.1&2, not due out until mid-2014, is for Pfizer and consultants to do a scaled up pilot test of the leading remediation candidates during 2013.

These candidates involve both heating the tarry and crumbly impoundments (in place) to drive off (and then capture) the VOCs (volatile organic compounds like benzene); and, second, stabilizing and solidifying (in a binder cement) the VOCs.  It is possible (and probably better) that both be employed.  A big question is whether EPA will require the treated materials to then be removed from these impoundments which are both quite close the the Raritan River.  EPA and Pfizer want to see the technical results of the pilot tests before deciding.  CRISIS may take a preliminary position on this issue since the Raritan River will be faced with potential safety concerns, especially under flood conditions, if the treated and solidified material is left in place.  (See also item #4 below on the Feb. 27 Progress Report Meeting on Imp. 1&2 Study.)

3) Positive Data on Reduced Benzene Contamination in River:


It should be recalled from local media news (in 2011 and early 2012) that benzene and other organic contaminants were found to be seeping at high concentration from the ground near Imps.1&2, and entering the Raritan River through groundwater at very unacceptable concentrations of over 100 parts per billion (ppB) at nearby river locations.  First emergency response was carbon filtering bags (later removed). The medium-term plan of action adopted by Pfizer, approved by EPA, was three-fold: digging an interceptor trench from which the contaminated ground water could be pumped to a treatment facility; installing a dedicated groundwater treatment facility near Imps.1&2; and building a slurry wall (down to bedrock), essentially around these impoundments.  These were completed in Spring 2012.  (The dedicated groundwater plant is a modular one, so it was installed quickly.  A permanent treatment plant, something that CRISIS had pushed for some years, is in planning.)  Pfizer has spent over $10 million on these mitigation steps so far.

Results to date are clearly positive.  The old seeps themselves are not seen because of the slurry wall installation, but the groundwater continues to be contaminated.  The encouraging aspect is that measurement of benzene in the river at points quite close to impoundments 1&2 are now (January 2013 sampling) in the low part per billion range (roughly 1 ppB), where they were previously in the 200 ppB range before the groundwater-mitigation projects. However, this much improved, lowered concentration is still above the regulatory 0.15 ppB level. During 2013, the levels of benzene in the river are to be monitored to see if the situation improves further.  (Long-run, the answer will be the still to be determined remediation plan for Imps.1&2 discussed in item 2 above.)  CRISIS thinks further intermediate term action might be required if the downward trend in benzene is not sustained.

Up-river (westerly) from the Impoundment 1&2 location, where the water company intake is located, the January 2013 sampling data reported by Pfizer indicate no detectable level of benzene.  Also at sampling points roughly a half-mile down-river (easterly) from impoundments 1,2, the levels of benzene have been lower (roughly the 0.15 ppB regulatory limit) than in vicinity of Imps. 1&2.

A more detailed study of sampling data changes and causes is being made by our Technical Adviser, and will be discussed in his coming March 2013 TA’s Report.

4. Progress Update Meeting on Feb. 27. 2013:


CRISIS hosted, under EPA auspices at its location in Edison, a Progress Report Meeting (technically oriented) for primary stakeholders on Laboratory Treatability Studies for Impoundments 1&2.  Invited were environmental organizations, local government representatives, and local business representatives.  Pfizer and CH2Mhill were the main speakers.  A separate report on this meeting will be prepared for our website.  (Our Treasurer, John Tucciarone, computerized the mailing lists required to do invitations and reminders for the meeting, without which we could not have pulled it off.)

CRISIS ORGANIZATIONAL HIGHLIGHTS:

TAG Grant Renewal from EPA:  Renewal of our TAG (Technical Assistance Grant) was received effective Jan. 25, 2013 for $50,000 to run through Aug. 31, 2015.  Most of this money is dedicated to paying our TA for his work.  A small portion is budgeted for website development.  We are required to provide $12,500 of “in-kind” (non cash) member contributions over the course of this grant extension.

CRISIS hired Dr. Ira Whitman, P.E. (Ph.D. in Environmental Engineering from Johns Hopkins University) as our new technical adviser (TA) commencing on Nov. 12, 2012 (he was able to attend the Nov. 14 EPA meeting).  We also interviewed two other very qualified candidates and developed a quantitative scoring matrix, submitted to EPA, to support our hiring evaluations.  We continue (through our TA) to monitor reports and data about the site issued by Pfizer, EPA and DEP.

Our new website (www.crisistoxicwatch.org) went into action in Sept. 2012.  It was developed by Casey Kittel, a member, who continues to manage the site.

Our founding Exec. Director, Walt Sodie, is currently on leave of absence to allow him time to work on his other business activites.
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Monthly Technical Report by CRISIS TA
February 2013

MONTHLY TECHNICAL REPORT
AMERICAN CYANAMID SUPERFUND SITE


CRISIS Inc.
Ira L. Whitman, P.E., PhD Technical Advisor


February 2013

    EPA’s monthly status update meeting with CRISIS, Inc. was held on February 11, 2013.  Ross Stander and Dr. Ira Whitman participated on behalf of CRISIS, Inc.

Impoundments 1 &2, Focused Feasibility Study

    Pfizer’s Focused Feasibility Study, Draft Laboratory Treatability Study Report for Impoundments 1 & 2 is presently under review by EPA’s office of Research and Development.  Comments from EPA are expected in March.  The results of the treatability study will be presented by Pfizer and its consultant, CH2MHill at the CRISIS project update meeting on February 27.

    Pfizer will be meeting on February 21 with NJDEP to review permit requirements for air emissions for the 2013 field pilot demonstration planned for September 2013.  The 30% design phase will be discussed by Pfizer with EPA on February 13.  On February 25 Pfizer will be giving EPA a preview of its February 27 presentation; CRISIS will attend.


Impoundments 1 & 2 Ground Water Removal Action

    Due to issues with toxicity testing, Pfizer has expanded its sampling activity for effluent from its modular ground water treatment plant.  EPA has approved, and NJDEP concurred with a Preliminary Corrective Action Plan for an investigation of the whole effluent toxicity testing procedure proposed.  Adjustments in ground water treatment have been made as a result of difficulties arising from freezing temperatures.

    Pfizer has presented EPA with a sampling plan for beneficial on-site reuse of soil displaced for construction of the removal system.

    Concentrations of benzene have decreased in the river; however in the areas of the benzene seeps concentrations still exceed the 1 part per billion standard.


Site-Wide Remedy

    Preliminary design plans are under discussion with EPA.  EPA conditionally approved a geophysics work plan designed to find the best locations for ground water capture wells.  A NPDES discharge permit application is presently being reviewed by NJDEP for a permanent future on-site ground water treatment system capable of treating all existing and future ground water (as distinguished from the new modular treatment facility near Impoundments 1 & 2 to treat VOC contaminated ground water before it is sent to SRVSA for final treatment).


Ambient Air Monitoring

    Third quarter perimeter air quality monitoring results have been presented to EPA showing no air quality concerns at present.  First quarter 2013 sampling took place on January 8, 2013.  Slightly elevated concentrations of benzene were detected in air quality measurements for Impoundment 2.  Pfizer will prepare an Ambient Air Quality fact sheet for use at CRISIS’ February 27 meeting.


Surface Water and Sediment Monitoring

    First quarter 2013 sampling took place during the week of January 7, 2013.  Additional sampling was conducted in the Cuckel’s Brook area made accessible by SRVSA’s rerouting of its discharge directly to the Raritan River.


Ground Water Monitoring Program

    Ground water monitoring was conducted during the week of November 26, 2012.  A draft report of sampling results will be submitted to EPA and NJDEP at the end of February.  Access will be given to consultants for a neighboring site, STS, to sample soil and ground water on the Pfizer property near their property boundaries.


Preparation for February 27 Meeting

    Ross Stander and Ira Whitman met with Pfizer and its consultants on February 1 to discuss the February 27 technical progress update meeting.  CRISIS presented a draft agenda for that meeting that was discussed in a conference call with EPA on February 7.  A consensus agenda will be finalized and distributed by CRISIS to conference attendees approximately 10 days before the February 27 meeting.


                Ira L. Whitman, P.E. PhD
                Technical Advisor to CRISIS, Inc.
                February 14, 2013


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M E M O R A N D U M
December 11, 2012

HURRICANE SANDY: A NO-FLOODING EVENT AT CYANAMIDE SITE


     Pfizer reports that Hurricane Sandy, and the subsequent Nor’easter rainstorm, during late October and early November this fall, resulted in no flooding of the Cyanamid site.  Serious to massive flooding of the site has been (and will continue to be) a serious worry in terms of potential damage to impoundment liners and flood protection berms on the site, if that should result in release of nasty materials into the Raritan River or brooks.

     During Hurricane Sandy and the Nor’easter winds caused minor damage to Impoundment 8 temporary liners and these are now being repaired by Pfizer.

     Another concern has been the possibility of power interruptions from flooding or winds that could impact the continuous pumping of contaminated groundwater to the treatment facilities, both the on-site Modular Facility put up by Pfizer during 2012, and at SRVSA (which is contiguous with the site).  While pumping interruption did occur in the September 2011 Hurricane Irene event, such was not the case during this fall’s storm events.

     CRISIS has set, as an important part of its conditions for full support of the ROD issued by EPA in Sept. 2012 for a large portion of the site (but not including the toughest part, Impoundments 1 and 2 right near the river), that several measures be taken to preserve pumping ability and berms during flooding.  These measures have not yet been acted upon by EPA, but we believe they will be during the engineering design phase (of the issued ROD) to take place over the next two years.  CRISIS will continue to press this issue, and other conditions we specified (see our letters to EPA under the “Current News” tab on this website, which may move to “Archives” tab at some point).

(R. Stander, for CRISIS, 12/11/12)
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M E M O R A N D U M
October 3, 2012

To: CRISIS Members and Interested Parties
From: Ross Stander, Exec. Chairman; Walt Sodie, Exec. Dir.
Summary of Recent Activity on American Cyanamid (Pfizer) Superfund Project and Within CRISIS

1. The CRISIS website is available to all for both recent news and ongoing information at:
www.crisistoxicwatch.org
The site was developed and established this summer by our member Casey Kittel. On it you can find for example the April 30, 2012 Supplemental Statement we sent to EPA during the public comment period (look under the Current News Tab). This was previously sent to most of you by email (June 28, 2012). This letter details the conditions set forth by CRISIS for our full support of the Remedy Alternative 4A of the EPA Proposed Plan for Sitewide Remediation, excluding Impoundments 1 & 2.
Also under Current News is the letter sent by BCOC (Bridgewater Cyanamid Oversight Comm.) which details what this panel would like to see added to the 4A Remedy.
2. ROD (Record of Decision) and Remedy:
The EPA issued the ROD for the site (excluding Impoundments 1 & 2) on September 28, 2012. Here is a direct link to the lengthy document:
http://www.epa.gov/region2/superfund/npl/american_cyanamid/pdf/americancy_rod.pdf
Please see the attachment for our initial response to the ROD.
Following is background on some of our work related to the site remedy that is contained in the ROD.
In May 2012, Ross presented our position/Conditions for full support of 4A to the Bridgewater BCOC (Chaired by Bob Albano). I was helped in the presentation and discussion by John Tucciarone (Director, Treasurer) and Jim Crane (Member from Somerville). Pfizer and its consultants actively participated there, providing technical information and answering questions. For example, there was discussion of Pfizer’s promise to fortify soil caps of the proposed 4A Remedy against the serious/massive flooding that has already occurred on the site. Such soil caps were much criticized by other groups at the March Public Hearing. Fortification of the soil caps is part of our “conditions” on 4A, and we will be pressing the issue of how Pfizer proposes to implement this design when it is presented. As noted the BCOC letter to EPA is on our website, and it is fair to say CRISIS and BCOC take similar (but not identical) positions regarding conditions on 4A.
These conditions on 4A are real and meaningful. Another example (besides fortification of soil caps) is that Pfizer move all principal threat wastes (PTWs) that lie outside the main plant (MP) berm to within that berm (effectively , a large flood-protective wall). The current EPA/Pfizer proposed plan leaves some PTWs outside that berm. After solidification and stabilization, these PTWs would be placed under soil caps (hopefully fortified). While the whole Cyanamid site is subject to massive flooding, as in hurricane Irene in 2011, at least the area behind the MP berm undergoes groundwater pumping which can then be treated for contaminants. Other flood related protections are included in our Supplemental Letter to EPA as discussed above.
The BCOC letter to EPA states that BCOC fully supports the work of CRISIS particularly in providing technical information and analysis developed by our TA (Tech Adviser) and evaluated by our Board, Exec. Director, and active members.
3. TAG Renewal and TA Hire Needed:
Our TAG grant period ended on June 30, 2012. During June, we applied to US-EPA for renewal of the EPA TAG grant, hopefully for another 3 years. At this writing EPA has requested additional information, which we are providing. The TAG grant has paid for our TA (tech adviser) for the prior two-decade period. Tom Germinario was our TA over that entire period. Tom decided, entirely of his own volition, not to return to the project if we get the TAG renewal. We clearly thank Tom for his many years of valuable service including and especially his many suggested improvements that were accepted by EPA and/or NJ-DEP. One of the most significant was Tom’s push over years for dedicated groundwater pretreatment (to be able to fully handle benzene and other nasty organic contaminants in the groundwater). Fantastic: this has now been accepted by and the first stage implemented (up and running) for Impoundments 1, 2 by Pfizer. We wish Tom continued success.
We are now in process of seeking and hiring a new TA, under proviso that EPA renews the grant. Serious new technical work, requiring community oversight, is expected to begin later this month, such as the feasibility evaluations for treating the benzene and other nasty materials in Impoundments 1, 2. You can find our RFP request for TA applicants on our website under the Tech Adviser tab.
4. Impoundments 1, 2 Area Groundwater Treatment:
As noted, Pfizer has implemented its dedicated groundwater pretreatment system (a modular plant) at the Impoundment 1, 2 area of the site, which is reported to be fully functional.
5. Benzene Seepage into Raritan river:
The abatement plan (see June 28 Update) to stop the highly publicized (during 2011 and at the EPA Public Hearing of March 8, 2012) seepage of benzene has been implemented by Pfizer, under EPA’s order and supervision. It includes and interceptor trench around Impoundments 1, 2; the modular treatment plant; and pumps for the groundwater in the trench to be sent to the treatment plant. Indications are that it is doing the abatement job. We are awaiting word on test measurements. The TAG renewal (for the new TA) would be very helpful in our monitoring of these tests. (Carbon filter bags, originally placed for the benzene emergency, have been removed recently, as no longer needed.)
6. Impoundments 1, 2 Long Term Remedy (Focused Feasibility Study-FFS)
The current, interim abatement process for groundwater seepage from these two impoundments (the most dangerous and hardest to remedy on the site), will eventually be replaced by treatment and removal of these dangerous materials. The FFS for this long term remedy (see June 28, 2012 Update) is not due until mid-2014. This is a delay from the original schedule, which we are told will allow more complete evaluation of the treatability plans even at a field testing level. We are expecting to see some reports on these treatability lab studies, possibly later this month.
7. Air Monitoring from Impoundments 1, 2 were done July 18-20. CRISIS is waiting to see that data.

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R E S P O N S E
September 2012

CRISIS Response to EPA Record of Decision (ROD), September 2012, for Former American Cyanamid Superfund Site, Bridgewater, New Jersey

The ROD does not satisfactorily respond to all of the points we outlined regarding measures to withstand flooding.  It did not directly address the following conditions from the 4/30/12 CRISIS written Supplement Statement (supplementing our testimony from the 3/8/12 EPA public meeting):

The Site-wide Feasibility Study indicates that the caps to be used in the Main Plant area (now called the North Area) will be multi-layered and engineered to withstand the stress of periodic flooding. That will be done during the Remedial Design phase, and CRISIS will monitor the process closely.  However, the Record of Decision should require that the highest attainable engineering standards be used in constructing the caps.  In this regard, cost should not be a consideration.  No matter how high the cost, Pfizer must be required to design, engineer and construct the caps for maximum resistance to floodwaters.
The caps and the berm should be heavily armored at points of highest water flow velocity, as experienced during Hurricane Irene.

Additionally, the ROD does not respond to this “General” concluding statement:

Because of the complexity of the Cyanamid site, the large-scale distribution of hazardous waste in the impoundments and soils, and the threat of frequent flooding, EPA must impose the most stringent possible standards for the current phase of the remediation and vigilantly monitor every step of the remediation process.  Furthermore, EPA should require Pfizer and/or its successors to monitor the site in perpetuity (under EPA supervision) and to make repairs that may be required to meet the conditions of all Records of Decision issued for site remediation.  This would include the flood berm, impoundments, groundwater pumping system, interceptor trench, slurry wall, treatment facilities, effluent gates, etc.  If EPA deems it appropriate to assure compliance, Pfizer could be required to post a bond to protect the community in case of financial changes in the company’s future or sale of Pfizer or the Cyanamid site to another firm.  As stated above, cost should not be a consideration in these decisions.

However, the ROD did address our other conditions, each of which is satisfactorily covered:  

Long-term groundwater treatment should rely on an on-site system designed specifically for the site’s contaminants, NOT on the Somerset-Raritan Valley Sewerage Authority’s (SRVSA) municipal wastewater treatment system.
Interim groundwater treatment at the SRVSA should be subject to enforceable effluent limitations for VOCs and SVOCs.
Materials in the floodplain requiring direct contact, vapor or movement control should be relocated to the Main Plant area and covered by the appropriate engineered multi-layered cap.
All principal threat wastes should be consolidated in Impoundments 3, 4 and 5 for in-situ s/s treatment.
Bench-scale testing should be conducted during the remedial design phase to determine the most effective combination of amendments, stabilizing agents and geogrids to be used in the in-situ s/s process.

We will continue to communicate with EPA and will strive to convince the agency to address the concerns noted above in the next round of the site remediation, which is the Remedial Design phase.
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M E M O R A N D U M
August 28, 2012
DATE: August 28, 2012

TO: Meeting Attendees
FROM: Vince D’Aco
RE: American Cyanamid Superfund Site, Bridgewater, NJ
Minutes – Monthly Update with CRISIS
August 20, 2012 Conference Call
ATTENDEES:
Mark Austin, USEPA Russ Downey, Pfizer Inc
Joseph Battipaglia, USEPA Elaine Richardson, Vita Nuova
Angela Carpenter, USEPA Vince D’Aco, Quantum Management Group
Melissa Dimas, USEPA
Walt Sodie, CRISIS
Chris Poulsen, Bridgewater Township
CC: Haiyesh Shah, NJDEP
Allan Motter, NJDEP
Michael Sivak, USEPA
The Agenda for this progress update is attached. The following bullets summarize the discussion and
action items from this meeting.
A. Impoundments 1 and 2 Focused Feasibility Study (FFS)
a. Russ indicated that a revised draft of the FFS Work Plan, responding to USEPA’s comments
of August 8, 2012, will be submitted to USEPA by August 27. Walt asked if USEPA
would distribute the Work Plan and Mark indicated that the final version would be distributed
after USEPA approval.
b. Russ provided an update on the laboratory treatability studies. The thermal treatment and
stabilization tests will be completed by August 24 and August 31, 2012, respectively. Preliminary
results have been positive, although there are technical challenges with both approaches.
c. Russ indicated that the draft laboratory treatability studies report will be available in October
2012. Mark said that Pfizer would present the results of the treatability work at a meeting
at the Site, possibly in October. He said that CRISIS and the Township will be invited
to this meeting. Russ asked whether CRISIS’ technical advisor would attend. Walt responded
that he hoped to have a technical advisor on board by that time.
B. Impoundments 1 and 2 Area Groundwater Removal Action
a. Russ indicated that the groundwater extraction trench and treatment system continues to
operate in compliance with the discharge permit equivalent.
MEETING MINUTES
AUGUST 20, 2012 PROGRESS UPDATE WITH CRISIS
AMERICAN CYANAMID SUPERFUND SITE, BRIDGEWATER, NJ
- 2 -
b. Russ reported that a revised arsenic design modification will be submitted to USEPA today.
The system will be constructed in two phases – the infrastructure to support the ion
exchange units will be installed now and the ion exchange units will be installed in the future
if necessary, i.e. if arsenic concentrations in the groundwater increase.
c. Russ indicated that the carbon bags installed on the seeps in March 2011 are being removed
because the groundwater collection trench and hydraulic barrier wall are now in
place to prevent further seepage into the river. This work will be complete by August 24.
d. Vince indicated that installation of a utility casing under the railroad tracks has been put
on hold due to unexpected field conditions, including interferences from a New Jersey
American Water pipeline and several fiber optic lines. Options are being evaluated for
providing power via overhead power lines. This is not interfering with operation of the collection
trench and treatment system, which are powered from diesel generators.
C. Ambient Air Monitoring Program
a. Russ reported that the first sampling event was conducted on July 18-20, 2012 and that
analytical data is starting to arrive. The data is being tabulated and will be compared with
screening levels. The results will be shared with USEPA and NJDEP soon.
D. Surface Water & Sediment Monitoring Work Plan
a. Russ reported that the surface water and sediment monitoring work plan and QAPP were
approved by USEPA on August 10 and that the first round of sampling was conducted
during the week of August 13, 2012. Walt asked for an electronic copy of the work plan
and QAPP – Vince will provide this.
E. Groundwater Monitoring Program
a. Vince will send an electronic copy of the First Half 2012 Semi-Annual Groundwater Monitoring
Report to CRISIS.
F. Other Discussion
a. Walt indicated that CRISIS has developed a demo website and asked if anyone was interested
in seeing it. Melissa asked for the website link.
G. The next CRISIS progress update is scheduled for September 17, 2012 at 11:00 a.m. An agenda
will be distributed on the Thursday prior to the call.
Wyeth Holdings Corporation
American Cyanamid Superfund Site Remedial Program
Status Update Meeting with CRISIS
August 20, 2012 at 11 a.m.
AGENDA
Phone number: 877.580.3949; Access Code: 52451906
A. Impoundments 1 and 2 Focused Feasibility Study (FFS)
a. Revised Draft FFS Work Plan: USEPA comments provided 8-Aug-12
b. Lab Treatability Studies: Ongoing; Draft Report by Oct 2012
c. Technology Evaluation: Ongoing; Complementary to Lab Treatability Studies
d. Thermal/Solidification Bench-Scale Study Update
B. Impoundments 1 and 2 Area Groundwater Removal Action
a. Start-up of groundwater extraction and treatment system initiated 11-May-12
b. Arsenic treatability study: Ion Exchange modular unit to be installed for As treatment option
c. Jack & Bore for new utilities below railroads complicated by NJAW line and fiber optics – New
design underway and subsequent railroad approval will be required
d. Continued improvements underway for treatment system operation and maintenance
C. Ambient Air Monitoring Program
a. 2Q12 sampling event occurred 19/20-Jun-12
D. Surface Water & Sediment Monitoring Work Plan
a. Revised Work Plan and QAPP approved by USEPA on 26-Jul-12 and 10-Aug-12, respectively
b. 3Q12 sampling event occurred during week of 13 thru 17-Aug-12
E. Groundwater Monitoring Program
a. Semi-Annual GWMR submitted to USEPA/NJDEP on 1-Aug-12
Next Meeting: 17-Sept-12 (3rd Monday of month) at 11 a.m.
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M E M O R A N D U M
June 28, 2012
Date: Thursday, June 28, 2012, 11:40 AM


TO: CRISIS Members & Interested Parties

FROM: Walt Sodie, Executive Director

 

Here is a summary of recent activity on the project.

 

1. Site Remedy:  USEPA is in the process of developing a Record of Decision (ROD) for the site, with the exception of Impoundments 1 & 2 (more on them below).  The decision will establish the remedy for this phase of project, which will be implemented over a period of several years.  The ROD is expected to be issued in the fall, possibly as early as September.  It will be based on the Sitewide Feasibility Study (FS) and the Proposed Remedial Action Plan (PRAP), which were the focus of the March 8, 2012 EPA public participation meeting that several of you attended, as well as further written comments that were submitted up to the end of the public comment period on May 15. To augment our March 8 testimony, CRISIS submitted a Supplement Statement to EPA on April 30 (distributed to most of you via e-mail update on May 3).  While no formal procedures exist for expressing our opinions on the remaining phases of the FS/PRAP/ROD process, CRISIS will continue to speak out, seek meetings with EPA and pursue whatever steps are available to us if we take exception to any of the decisions.

 

2. Groundwater:  One of our prime objectives during the 19+ years in which we have been working on the site has been an upgrade in the treatment of contaminated groundwater.  A positive step in that direction has occurred since the May 3rd update. Pfizer recently began treating some of the groundwater in its own, on-site interim treatment plant, which is operating under a Permit Equivalent issued by NJDEP.  The on-site facility was trigged by item #3 below, and the groundwater currently being treated by Pfizer is in connection with that program.  The treated water is being discharged into Cuckhold’s Brook, which flows into the Raritan River .  CRISIS will review monitoring reports from the two waterways when they become available in the near future.  Because the interim plant’s capacity is limited, the Somerset-Raritan Valley Sewerage Authority will continue to treat much of the site’s groundwater. However, if the current operation is successful, Pfizer will seek approval to build a permanent plant that could handle all site groundwater.

 

3. Impoundments 1 and 2 Area Groundwater Removal Action:  In late 2010, benzene-contaminated groundwater was discovered seeping into the Raritan River in the vicinity of Impoundments 1 and 2.  Pfizer entered into an Administrative Settlement Agreement with EPA to correct the problem.  The abatement plan included placement of carbon filters, building an interceptor trench and slurry wall, and installation of pumps to remove the groundwater for treatment.  Pfizer and EPA believe the steps have cut off the seepage into the river but CRISIS is awaiting the next round of river-water testing before we issue a statement.

 

4. Surface Water & Sediment Monitoring Work Plan:  Although CRISIS has asked for more frequent testing of Cuckhold’s Brook and the Raritan River , this pending workplan calls for quarterly monitoring.  However, EPA and DEP have not yet issued final approval of the plan and both have scheduled web conferences with Pfizer and its consultants to discuss agency concerns.  CRISIS will continue to monitor these developments.  If the next round of testing indicates any cause for concern, we will push for follow-up testing well before the scheduled three-month timetable.

 

5. Impoundments 1 and 2 Remedy:  Because these impoundments contain the heaviest concentrations of the most toxic contaminants on the site, they are being addressed via a separate Focused Feasibility Study (FFS).   While the full study is not expected to be ready until mid-2014, critical testing will be conducted during that time, including laboratory and field testing of in-place thermal treatment and solidification/stabilization of contaminants.  In earlier phases of the site remediation, testing was not conducted until after feasibility studies were issued.  Thus, while the target date for the FFS is later than we originally anticipated, the selection of a remedy should occur more quickly after its completion than was the case with the previous feasibility studies.  CRISIS will monitor each phase of the FFS process.

 

6. Flood Emergency Procedures Plan/Flood Management Response Plan:  EPA is currently reviewing these plans, which deal with operational response prior to, during, and following a flood.  CRISIS’s Supplement Statement to EPA (point #1 above) asked EPA to order measures to protect against future flooding as part of the site remedy, which is separate from the Flood Emergency Procedures Plan/Flood Management Response Plan.  While some of the site infrastructure was upgraded following Hurricane Irene, the height of the berms has not been increased to protect against a 500-year flood, as CRISIS requested.  EPA has declined to say whether that issue and the others we raised will be part of the site remedy but indicated that CRISIS’s comments will be addressed in the Responsiveness Summary that will be issued with the ROD.  We will be vigilant on these flood issues.

 

7. Non-Technical Activity:  With the Superfund project having moved back into high gear early this year, CRISIS has been expanding our membership and adding to our list of interested parties.  If any of you would like to become more active in what we are doing, please contact me at the e-mail address above or CRISIS Chairman Ross Stander at tensor_metrix@yahoo.com.  In addition to any other aspects of the project that may be of special interest to you, Ross is taking the lead on development of a CRISIS website and welcomes volunteers for help with that task.

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L E T T E R
May 12, 2012



The following is a response letter sent by the Bridgewater Cyanamid Oversight Committee (BCOC), chaired by Robert Albano, to the EPA during the recent public comment period following the March 2012 public meeting regarding the site remediation. 

 

Robert E. Albano

1149 Papen Rd

Bridgewater NJ 08807

908 658 3387  bobalbano@yahoo.com

May 12, 2012

 

 

 

 

Joseph Battipaglia

Remedial Project Manager

USEPA

290 Broadway, 19th Floor

New York, NY 10007-1866

 

 

Mr. Joseph Battipaglia

Re: written response on EPA Public Comment on American Cyanamid Superfund Feasibility Study

 

On behalf of the Bridgewater Cyanamid Oversight Committee, I wish to thank you for efforts you and your associates are making to remediate the site. Thanks for the presentation you gave the Committee in Dec 2011 and for the information you provided at the March public hearing.

This letter is the position and recommendation of the Bridgewater Cyanamid Oversight Committee.

Very Truly Yours,

 

Robert Albano

Chair- Bridgewater Cyanamid Oversight Committee

 

 

 

Att: 1

 

CC: Bridgewater Mayor and Township Council

        Russell Downey – Pfizer Project Manager

        Walt Sodie – CRISIS

        BCOC members

 

 

 


To: Mr. Joseph Battipaglia

Subject: written response on EPA Public Comment on American Cyanamid Superfund Feasibility Study

From: Robert Albano, Chairman – The Bridgewater Cyanamid Oversight Committee

Date: May 12, 2012

 

 

The Bridgewater Cyanamid Oversight Committee, BCOC, was formed with assistance of the Mayor and Township Council of Bridgewater in May 2011. The BCOC consists (1) of local residents of diverse backgrounds and interests.  Many members are long time residents and community leaders, some of whom were already familiar with the American Cyanamid site and situation.  The Committee was assembled to study the proposed alternatives and to evaluate the benefits and liabilities of each.  Its responsibility is to provide input to the EPA, DEP, Pfizer and the community on cleanup and future use of the property.

 

The Committee has met numerous times during the past year and has met with many people including EPA officials, Pfizer personnel and consultants,  CRISIS members, Bridgewater Township officials and local interested parties.  The Committee has studied background information, the alternative proposals for cleanup and visited the site on several occasions.  This letter expresses recommendation of the Bridgewater Cyanamid Oversight Steering Committee as a whole and not of any one member. This letter expressly indicates the Committee’s support for the proposed remedy with the additional conditions stated below.

 

The American Cyanamid Superfund site has been under review for almost 30 years.  Exhaustive study has been conducted during that time leading to the present EPA identification of the preferred alternative.  Pfizer, the current site owner, acquired the property in a corporate acquisition, never operated this site nor contributed to the existing conditions.  In all our contacts with Pfizer to date, they have accepted responsibility for implementing an effective remediation plan and returning the site to a safe and useful property. 

 

The Bridgewater Cyanamid Oversight Committee strongly supports the implementation of Alternative 4A.  This alternative provides a balanced approach offering several benefits.  It should make this site safe for residents of the surrounding area as well as for those living downstream from the site.  Alternative 4A uses proven conventional technologies that can be implemented in a reasonable period of time.  Since this alternative requires limited surface disturbance and soil relocation, it should minimize risks for residents during construction.  The proposed 4A plan is consistent with EPA’s RTU Initiative per the EPA Web site which encourages reuse of the property with a limited section having potential for commercial development and other areas available for active and passive recreation.  Alternative 4A may also reduce the impact of future floods. Plan 4A has the additional advantage of being a living document that will accommodate use of new technologies and approaches as these are discovered. The Plan also will begin the clean up in a more timely and effective manner than other Plans under discussion,

 

The BCOC is working closely with and fully supports the effort of CRISIS, a local citizens group, which has monitored the cleanup for nearly 18 years, to continue its work under and extension of  its TAG grant. CRISIS has and does serve as an information source and provides technical expertise on the site cleanup for the entire community and region. CRISIS has reviewed Proposal 4A. BCOC is primarily concerned with the future use consistent with safety of the community and surrounding areas. BCOC relies on CRISIS as a technical resource and BCOC supports the recommendations that CRISIS has put forward to improve Plan 4A. 

 

The BCOC suggests the following be added to Plan 4A

  1. Remove all PWT from the river banks to impounds behind the existing berm regardless of the risk assessments
  2. Maintenance of the existing berm toProvide for stabilization of VOC/SVOC with evidence of effectiveness through Simulation, Bench and Field testing prior to implementations
    1. control >100 yr storms by retaining excess flood waters
    2.  provide an added level of safety against accidental leakage or seep from the impounds

  3. Full treatment of ground and surface water on site with a specifically designed facility and not use SRVSA for water treatment
  4. Ensure that all impounds and impacted areas are stable in the 500 yr storm for leaching, scouring, erosion or uplifting.
  5. Protection of SRVSA and American Water from contamination from the site
  6. Redundant capability to ensure that power to operations is not compromised by adverse weather, flood, or power interruption, such as 2011 Storm Irene.
  7. Financial bonds for continuous operation, monitoring and maintenance of the site
  8. Separation of impounds 1 and 2 from FS4A for a separated feasibility study
  9.  Implement Plan 4A consistent with “Return to Use” principles that support the economic value of the site as commercial ratable status. The Committee recognizes that much of the site cannot be returned to commercial use but support identification of areas in the Northern end of the property for commercial development and the central portion of the property for recreation uses.

 

The BCOC believes that moving forward with Plan 4A represents the best approach to cleanup of the site that has been on hold for 10 years. We disagree with those who suggest that the plan be scrapped for more study. We agree with CRISIS, Bridgewater Township, Somerset County, Pfizer and EPA   assessments that Alternative 4A offers the best level of safety and timeliness.

 

Questions or comments may be addressed to:

Robert Albano

1149 Papen Rd

Bridgewater NJ 08807

bobalbano@yahoo.com

Footnotes:

1 Bridgewater Cyanamid Oversight Committee members

 

Member

Community

Alan Kurydla

Bridgewater Township Council President

Chris Poulsen

Bridgewater Health Director and Liaison to Bridgewater Township

Gene Yuliano

MD and Member Bridgewater Health Bd

George Schofield

Business owner- across from site, Rescue Squad member, Long time resident

Jim Anderson

Bridgewater resident

Jim Rokosny

Chairman Bridgewater Environmental Commission

John Schmitt

Chairman Bridgewater Economic Development Committee

Joseph Lefreiri

Commissioner, SRVSA

Michelle Lawrence

Member Bridgewater Recreation Board

Nitin Apte

Environmental Consultant and resident

Robert Albano

Chairman and former Bridgewater Township Council member, current Planning Bd member

Ross Stander

Chairman - CRISIS

Susan Dorward

Bridgewater Sustainability Task Force

 

 

            



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L E T T E R
April 30, 2012

C R I S I S

 


                                                                                  925 Brown Rd.   Bridgewater, NJ 08807

 

April 30, 2012                                                            (Sent via e-mail this date)

 

 

Joseph Battipaglia

Remedial Project Manager

USEPA Region 2

battipaglia.joseph@epa.gov

 

Dear Mr. Battipaglia:

 

We are submitting this communication in follow-up to statements we entered into the record at the March 8, 2012 EPA-conducted public hearing on remediation plans for the American Cyanamid (Pfizer) Superfund site.  The points that follow supplement oral statements that were given by CRISIS Technical Advisor Thomas Germinario, CRISIS Board Chairman Ross Stander and myself, and Mr. Germinario’s letter of March 6, 2012 to you (“Re: Site-Wide Feasibility Study and Proposed Remedial Action Plan, American Cyanamid Superfund Site”).  Some of the material reiterates sections of our March 8 presentations that require more emphasis. 

 

CRISIS recognizes that EPA is cognizant of some of the points to be made below and that EPA may have already planned to implement some of the suggestions.  They are included not only for EPA’s consumption but also for review by other interested parties.

 

While CRISIS does not object to EPA’s preferred remedy of solidification/stabilization (S/S), we strongly believe that the plan should be bolstered by implementation of the measures that follow.

 

 

Conditions for Implementing Solidification/Stabilization (S/S) Remedy

 

CRISIS wishes to stress the importance we place on the five bulleted points on page 3 of Mr. Germinario’s letter referred to above.  These proposed steps, repeated immediately below, not only are conditions for our support of EPA’s preferred remedy but are actions we believe are essential for inclusion in the Record of Decision:

 

  • Long-term groundwater treatment should rely on an on-site system designed specifically for the site’s contaminants, NOT on the Somerset-Raritan Valley Sewerage Authority’s (SRVSA) municipal wastewater treatment system.
  • Interim groundwater treatment at the SRVSA should be subject to enforceable effluent limitations for VOCs and SVOCs.
  • Materials in the floodplain requiring direct contact, vapor or movement control should be relocated to the Main Plant area and covered by the appropriate engineered multi-layered cap.
  • All principal threat wastes should be consolidated in Impoundments 3, 4 and 5 for in-situ s/s treatment.
  • Bench-scale testing should be conducted during the remedial design phase to determine the most effective combination of amendments, stabilizing agents and geogrids to be used in the in-situ s/s process.
    • The caps and the berm should be heavily armored at points of highest water flow velocity, as experienced during Hurricane Irene.
      • LTTD is a poor choice for a heterogeneous mix of volatile and semi-volatile organic compounds (VOCs & SVOCs).  LTTD uses heat to vaporize the organic contaminants so that they are driven off the waste and captured for treatment. Therefore, LTTD has to operate in the temperature range between the boiling point and the combustion temperature of the organic compound.  Since SVOCs have a much higher boiling point than VOCs, completely vaporizing a mix of VOCs and SVOCs would require a higher temperature than would be safe to use, because it would be too close to the flashpoint of the VOCs.

Our conditions for groundwater treatment are crucial.  The impoundments to be treated with S/S are located in the Main Plant Area where the groundwater flow is controlled by the bedrock pumping wells. Therefore, any leaching of organics will be drawn down into the groundwater recovery system and sent for treatment.  Currently, this treatment is being done at the SRVSA, with which CRISIS is not satisfied. (We have repeatedly asked for an engineering analysis of SRVSA’s capabilities to treat VOC/SVOC wastes and never gotten any response.  The typical municipal-type sewage treatment plant is not equipped to remove these wastes without some degree of pre-treatment.)  If CRISIS is successful in getting Pfizer to design and build a state-of-the-art, on-site dedicated groundwater treatment plant, the site will then have a much stronger system that will protect the environment, even if some leaching of organics occurs from the S/S impoundments.

The condition calling for bench-scale testing (done in a simulated environment) is also critical; its implementation would assure that the best possible S/S technology will be used.  Here is more detail on bench-testing techniques CRISIS is asking EPA to order:

 

We favor re-remediation testing of various types of S/S treatment to determine the optimal method of immobilizing the unique mix of organic contaminants at this site. There are leaching procedure test methods that have been approved by USEPA for simulating how the S/S treated material will perform in its intended disposal site. These leaching procedures can accurately predict the rate at which organic compounds will leach under the influence of simulated rain and groundwater.

 

 

Flooding and the Danger of Cap Erosion

 

A few speakers at the March 8 EPA public hearing cited frequent flooding as an argument against S/S, contending that floodwaters will wash away caps covering the waste impoundments and release hazardous waste into the water.

 

While the entire Cyanamid site is in the Raritan River’s floodplain, there is a substantial difference between the risks associated with wastes stored inside and outside the Main Plant area. As discussed above, the groundwater in the Main Plant area is controlled by the bedrock pumping system and can be treated if contaminants escape as a result of flooding. Also, the Main Plant is surrounded by a flood dike which slows the rate at which flood waters enter and recede from that area. Therefore, the risk of contaminants being washed away by the uncontrolled force of floodwaters is much less within the Main Plant area than outside it.  Nevertheless, the threat demands that EPA impose rigorous conditions to mitigate flood damage

 

The Site-wide Feasibility Study indicates that the caps to be used in the Main Plant area will be multi-layered and engineered to withstand the stress of periodic flooding. That will be done during the Remedial Design phase, and CRISIS will monitor the process closely.   However, the Record of Decision should require that the highest attainable engineering standards be used in constructing the caps.  In this regard, cost should not be a consideration.  No matter how high the cost, Pfizer must be required to design, engineer and construct the caps for maximum resistance to floodwaters.
Additionally, we request that the following conditions be included in the Record of Decision:

 

  • The impoundments must be much better protected than in recent extreme flooding.  Specifically, the berm around the main plant area must be improved to withstand a “500-year” flood, a magnitude that has been reached or approached several times at the site.  The improvement should be both in height and strength of the berm. 

 

  • The Remedial Design must specify a means to firmly secure the S/S material under the soil caps to prevent contaminants from being washed out in serious, repeated floods.

 

 

  • The ground water pumping system must be protected against electricity failure in storms, including maintenance of large backup generators on high ground, and allowing for proper water runoff into the outflow brook.

 

 

Low Temperature Thermal Desorption Inappropriate for Cyanamid Site

 

A small number of environmental groups with no previous involvement at the site called for LTTD to be used for the most severely contaminated sections: impoundments 3, 4 and 5. 

 

LTTD involves in-place thermal treatment that causes contaminants to separate (desorb) from the soil without burning.  CRISIS’s extensive review of engineering and environmental reports and studies indicates that the process is not a suitable remedy for impoundments 3, 4 and 5. 

 

CRISIS has been studying and responding to actual and potential remedies for this highly contaminated site for over 20 years and has substantial knowledge of the waste characteristics and past attempts to treat a wide range of deadly substances there.  To document our position that LTTD is not the appropriate remedy for these impoundments, CRISIS developed the following points from our review of engineering and environmental reports and studies*:

 

 

  • Just one example: The Sidney Tar Sands site in Nova Scotia, Canada called for remediation of a number of tar ponds having a heterogeneous mix of VOCs and SVOCs, including Benzene, Xylenes, Toluene and Naphthalene, which are also the principal organic contaminants of Cyanamid’s Impoundments 3, 4 and 5.  After extensive studies, the selected remedy (2007) was solidification/stabilization (S/S) technology, not LTTD.

 

  • Anyone with any degree of familiarity with Impoundments 3, 4 & 5 would conclude that LTTD is not a good fit.  It works well primarily with soils that are contaminated with PHC (petroleum hydrocarbons).  The contaminants have to be relatively homogeneous because there's a specific range of temperatures that needs to be applied to volatize the contaminants while not oxidizing (burning) them.  Also, the sticky tar consistency of this waste (Impoundments 3, 4 & 5) would make a mess in an LTTD system.  The tar would have to be processed into a fine granular material.  That would be a difficult task in itself, and would almost surely result in large fugitive emissions of VOCs (Volatile Organic Compounds) during the material processing.

 

 

General

 

Because of the complexity of the Cyanamid site, the large-scale distribution of hazardous waste in the impoundments and soils, and the threat of frequent flooding, EPA must impose the most stringent possible standards for the current phase of the remediation and vigilantly monitor every step of the remediation process.  Furthermore, EPA should require Pfizer and/or its successors to monitor the site in perpetuity (under EPA supervision) and to make repairs that may be required to meet the conditions of all Records of Decision issued for site remediation.  This would include the flood berm, impoundments, groundwater pumping system, interceptor trench, slurry wall, treatment facilities, effluent gates, etc.  If EPA deems it appropriate to assure compliance, Pfizer could be required to post a bond to protect the community in case of financial changes in the company’s future or sale of Pfizer or the Cyanamid site to another firm.  As stated above, cost should not be a consideration in these decisions.

 

Thank you for your consideration of this communication.

 

Walt Sodie

Executive Director

CRISIS

 

 



 

* Following is a list of references for our position that S/S technology is more appropriate than LTTD for impoundments 3, 4 & 5. While not every one of the sources provided the explicit information contained in the three bullet points regarding LTTD, they indicate the difficulties of applying LTTD to mixed wastes. Some of the sources were not directly researched by CRISIS but were cited by reference material that was examined.

 

 

http://en.wikipedia.org/wiki/Sydney_Tar Ponds.

 

http://www.epa.gov/oust/cat/LTTD.HTM.

 

Applying Solidification/Stabilization for Sustainable Redevelopment of Contaminated Property - (Charles M. Wilk LEHP, QEP, LEED AP, Program Manager, Waste Treatment, Portland Cement Association.

 

Conner, J.R. Chemical Fixation and Solidification of Hazardous Wastes; Van Nostrand, Reinhold: New York.

 

Technology Resource Document—Solidification/Stabilization and Its Application to Waste Materials; EPA 530/R-93/012; U.S. Environmental Protection Agency.

 

Innovative Treatment Technologies for Site Cleanup: Annual Status Report, 12th Edition; EPA 542-R-07-012; U.S. Environmental Protection Agency.

 

Engineering Bulletin—Solidification/Stabilization of Organics and Inorganics; EPA 540/S-92/015; U.S. Environmental Protection Agency.

 

Weitzman, L.; Conner, J.R. Descriptions of Solidification/Stabilization Technologies. In Immobilization Technology Seminar—Speaker Slide Copies and Supporting Information; CERI-89-222; U.S. Environmental Protection Agency.

 

Conner, J.R. Guide to Improving the Effectiveness of Cement-Based Stabilization/Solidification; EB211; Portland Cement Association: Skokie, IL.

 

Pozzolan—a siliceous or siliceous and aluminous material which in itself possess little or no cementitious value, but which will, in finely divided form and in the presence of moisture, chemically react with calcium hydroxide at ordinary temperature to form compounds  possessing cementitious properties. Standard Terminology Relating to Hydraulic Cement, ASTM C 219-98.

 

Stabilization/Solidification of CERCLA and RCRA Wastes—Physical Tests, Chemical Testing Procedures, Technology Screening, and Field Activities; EPA 625/6-89/022; U.S. Environmental Protection Agency.

 

Einhaus, R.L.; Erickson, P. Fate of Polychlorinated Biphenyls (PCBs) in Soil Following Stabilization with Quicklime; EPA 600/2-91/052; U.S. Environmental Protection Agency.

 

Guide Specification for Military Construction—Solidification/Stabilization of Contaminated Material; CEGS-02445; U.S. Army Corps of Engineers.

 

Delisio, R. Cement-Based Solidification/Stabilization on Brownfield Sites in New Jersey, USA Presented at the Cement Association of Canada, Remediation Technology Workshop: Solidification and Stabilization Treatment, Toronto, Ontario, Canada, (unpublished).

 

Wilk, C.M.; DeLisio, R. Solidification/Stabilization Treatment of Arsenic- and Creosote-Impacted Soil at a Former Wood-Treating Site; SR99.

 

Wilk, C.M.; Germano, M. Remediation of Lead- and Petroleum-Contaminated Soils at a Boston Brownfield Site Using Cement-Based Solidification/Stabilization. In Proceedings of the International Containment & Remediation Technology Conference, Orlando, FL.

 

            


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