ASSESSMENT OF CONTROLS OVER
EMERGENCY REMOVAL ACTIONS AT
METHYL PARATHION SITES

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COVER

Office of Inspector General
Report of Review


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ASSESSMENT OF CONTROLS OVER EMERGENCY REMOVAL ACTIONS AT

METHYL PARATHION SITES

E1SFB7-06-0020-7400069

September 23, 1997

Inspector General Division
Conducting the Audit:

Regions Covered:

Program Office Involved:

Central Audit Division
Dallas, Texas

Regions 4 and 6

Emergency and Remedial
Response Division

MEMORANDUM

MEMORANDUM


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SUBJECT: Results of Assessment of Controls Over Emergency
Removal Actions at Methyl Parathion Sites
Report No. E1SFB7-06-0020-7400069

FROM:	Elissa R. Karpf

Deputy Assistant Inspector General
for External Audits

TO:	Timothy Fields, Jr.

Acting Assistant Administrator

for Solid Waste and Emergency Response

Attached is our assessment of the controls over disbursements and other
activities related to emergency removal actions at methyl parathion sites. Our
assessment indicates that Agency controls over several aspects of the removal process
could be strengthened with clarification of existing guidance or with the development
of additional national guidance. The attached discussion focuses on:

the potential for inadequate resources and procedures for implementing
a new sampling approach,

inconsistencies in decisions to conduct cleanups at businesses,
the potential for fraudulent and excessive relocation costs,
inconsistencies in documentation of personal property records, and

the potential for increased costs and delays in completion of
residential restorations.


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Also included are suggestions that we believe will provide greater consistency
and strengthen the Agency's controls in future similar emergency responses. We look
forward to receiving written comments with proposed actions that your office may take
in response to our suggestions within the next 120 days.

We appreciate the collaborative efforts of the Office of Emergency and Remedial
Response in providing us information and insight to facilitate our review. During
our field visits, we spoke with many individuals who were very receptive to our
observations and who expended considerable time and effort in protecting the health
of hundreds of families affected by the methyl parathion contamination. We commend
the efforts put forth by the individuals who assisted us. We believe the way the
Agency worked with the Office of Inspector General staff in discussing the problems
and identifying solutions demonstrates a shared commitment to improve Agency
operations and protect government funds.

If you or your staff have any questions, please contact Dave Boyce, Audit
Manager in our Dallas office, at (214) 665-6621.

Attachment

ATTACHMENT

ATTACHMENT

ASSESSMENT OF EMERGENCY REMOVAL


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ACTIONS AT METHYL PARATHION SITES

INTRODUCTION

Based on concerns raised by the Environmental Protection Agency's (Agency) program

officials, we conducted an assessment of controls over emergency removal actions at
methyl

parathion sites. The overall objective of the assessment was to determine the adequacy
and appropriateness of Agency policies and procedures to perform emergency removal
actions. In particular, we focused on those policies and procedures which addressed
sampling, relocation, decontamination, and restoration.

BACKGROUND

Methyl parathion is a highly toxic pesticide registered for use on several agricultural

crops and is restricted to outdoor use. This type of pesticide typically affects the

capability of the human central nervous system to regulate itself. Exposure, which may

occur through contact, inhalation, or ingestion, can cause serious illness and even
death.

Methyl parathion readily breaks down in the environment through a combination of natural
sunlight, water, and biological actions, but does not readily degrade indoors.

The Office of Solid Waste and Emergency Response (OSWER) issued Directive 9360.3-12,
dated

August 12, 1993, which provided guidance on the use of authority under section 104 (a) of

the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), as

amended, to conduct indoor response actions such as the methyl parathion emergency. This

directive clarifies that CERCLA section 104 authority should be used only in instances of

a release or threat of release of a hazardous substance into the environment and only
when

such release or threat of release poses a hazard to public health or welfare or the
environment. A finding of imminent and substantial endangerment of a pollutant or


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contaminant must also exist.

The Agency's initial involvement with methyl parathion contamination in residences was in
Lorain County, Ohio, in December 1994. Ohio health officials alerted the Agency that
hundreds of residences might have been contaminated with methyl parathion. The Agency,
using various resources, temporarily relocated 869 residents, and decontaminated and
restored 233 homes. Removal actions at the Lorain County site were completed in February
1996, at a cost of approximately $18,500,000.

Less than a year later, in November 1996, the State of Mississippi requested the Agency's
assistance in responding to a public health hazard posed by the illegal application of
methyl parathion in homes and businesses in and around Jackson County, Mississippi. One
month later, the State of Louisiana requested assistance for response to methyl parathion
contamination in the New Orleans area. Based on the experiences of Lorain County, the
Agency responded and tested the extent of contamination, relocated residents, and
decontaminated and restored residences and some businesses.

In May 1997, the State of Illinois contacted the Agency requesting assistance for
response

to methyl parathion contamination in the Chicago area. The Agency is in the process of
planning its proposed actions for the Chicago site.

The latest Office of Emergency and Remedial Response (OERR) Methyl Parathion Response
Status report, dated September 5, 1997, shows costs obligated for removal actions at each
state as follows:

Mississippi	$36,050,000

Louisiana	$17,800,000

Illinois	$ 5,500,000

In January 1997, Regions 4 and 6 contacted the Office of Inspector General (OIG) Office
of

Investigations (01) regarding allegations of irregularities in some residents' relocation


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applications in Mississippi and Louisiana. Through 011s involvement and discussions with
the Agency, we agreed to assist the Agency by assessing the adequacy of the policies and
procedures used by the regions throughout the various aspects of the removal process.

The removal process, which is generally initiated by calls from individuals to an
established Pesticide Hotline, consists of four phases:

sampling,

resident relocation,
decontamination, and
restoration.

A state agency collects wipe samples from high contact/high traffic areas in a residence
or business. Such areas are locations with an increased probability for repeated and
prolonged human contact with the potentially contaminated surface. A designated
laboratory then analyzes the samples for methyl parathion. Residents were originally
relocated based on health criteria developed and used by the Agency in Lorain County,
Ohio. Rapid relocation of residents and decontamination of the residence occurred if
methyl parathion from a wipe sample equaled or exceeded a certain level. The
decontamination and restoration procedures involve the removal of contaminated food and
fabric items; painting of contaminated surfaces; and removal and installation of
replacement carpeting, baseboards, furnace filters, cabinets, furnishings, and
non-structural building components which remain contaminated.

In May 1997, the Agency changed its criteria for relocating residents and decontaminating

residences. The change resulted from a determination made by the Methyl Parathion Health

Sciences Steering Committee that scientific relationships between levels of methyl

parathion found in residences and levels found in urine samples taken from residents were

not found to exist in other geographic locations as existed in Lorain, Ohio. The

differences were attributed to site-specific circumstances, such as spray technique,
house


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construction, and climate factors. In the absence of such site-specific correlations,
the

steering committee determined that methyl parathion levels in urine should become the
prime determinant for relocating residents to decontaminate residences.

SCOPE AND
METHODOLOGY

Our review focused on the ongoing and proposed removal actions at three primary sites:

(1)

the Jackson County, Mississippi site in Region 4; (2) the New Orleans, Louisiana site in
Region 6; and (3) the Chicago, Illinois site in Region 5. We coordinated our review with
OIG investigators already onsite in Mississippi and Louisiana to avoid duplication of
effort. We met with headquarters program officials in OERR, and program officials in
Regions 4, 5, and 6. We made visits to the Jackson County and New Orleans sites to meet
with the on-scene coordinators (OSC), emergency response contractors (ERCS), and
representatives from the U.S. Army Corps of Engineers (Corps). Additionally, we met with
the Agency for Toxic Substances and Disease Registry staff co-located with Region 6 and
representatives from the Mississippi State Department of Health (MSDH), the Louisiana
Office of Public Health, and the Louisiana Department of Agriculture and Forestry (LDAF).

To facilitate our review, we obtained memorandums from the Agency's Office of General
Counsel to verify the Agency's authority to conduct the removal actions. Also, we
obtained a copy of the EPA National Oil and Hazardous Substances Pollution Contingency
Plan ( NCP); the Uniform Relocation Assistance, Real Property Regulations for Federal and
Federally Assisted Programs; and EPA Guidance on Temporary Relocations During Superfund
Removal Actions to assess relocation criteria. We reviewed files maintained at both the
New Orleans and Jackson County sites to determine the effectiveness of administrative
controls over relocation benefits, reimbursement of personal property, and health effects
of the methyl parathion spraying.

This review, like all special reviews, was a short term study of Agency activities. It


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was not designed to be a detailed audit. Rather it was an information gathering survey

that sought to assist the Agency by providing an assessment of the adequacy of the

policies and procedures being followed for removal actions at methyl parathion sites.

Thus, it was more limited in scope than an audit and, as such, did not necessarily

encompass all generally accepted government auditing standards. Alternately, we
conducted

this review in accordance with the provisions of OIG manual chapter 118, Special
Assignments.

OBSERVATIONS
AND CONCLUSIONS

Our assessment indicates that the Agency could strengthen controls over several aspects
of

the emergency removal process with the clarification of existing guidance and the
development of additional specific national guidance. The lack of adequate national
guidance has resulted in:

the potential for inadequate resources and
procedures for implementing a new sampling
approach,

inconsistencies in decisions to clean up
contaminated businesses,

the potential for fraudulent and excessive
relocation costs,

inconsistencies in the documentation of
personal property items, and

the potential for increased costs and delays


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in completion of residential restorations.

We discussed these concerns initially with headquarters program officials in OERR, and
again during recent task force conference calls. In response, the Agency has issued
several new directives that address some of the areas of concern we have raised. However,
we believe that further improvements would strengthen Agency controls and further reduce
future instances of fraudulent activities related to methyl parathion cleanups.

IMPLEMENTATION OF NEW TESTING PROCEDURES

On May 16, 1997, OSWER issued Directive 9285.7-27 which provides guidance to the regions

for implementing a urine sampling protocol to test for excessive levels of methyl

parathion in residents' urine. The intent of the directive was to ensure that the
regions

applied consistent criteria in deciding what actions to take in response to methyl
parathion exposures.

In implementing the urine sampling protocol, the Agency did not adequately address:

resources to collect and analyze the samples,

resources for subsequent monitoring, and

procedures for disclosure and notification of
changes in residential occupancy.

The Agency delegated responsibility for testing methyl parathion levels in residents'

urine to state public health agencies but did not initially ensure that these agencies
had

adequate resources to collect urine samples and perform subsequent monitoring. OSCs in
Regions 4 and 5, and representatives from MSDH and LDAF, expressed concerns that the
public health services in Louisiana, Mississippi, and Illinois lacked the resources to
effectively administer the increased urine sampling and subsequent monitoring. They


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expressed further concerns that the Center for Disease Control in Atlanta might lack the
capacity to timely test the anticipated number of samples.

Additionally, the new protocol did not address the issue of disclosure and notification
when changes in residential occupancy occur. This notification and the associated need
for subsequent urine sampling might be critical for new occupants, especially those with
small children. A lack of clear guidance and sufficient resources for sample collection,
analysis, and monitoring has the potential for reducing the effectiveness of the program
as well as creating increased exposure and adverse health effects.

We recently learned that the Agency, as suggested in this assessment, has worked with the

appropriate state and local officials to gain the resources needed to meet the demands
for

urine sampling and analysis. Additionally, the development of a long term monitoring and
notification policy is still in progress.

CLEANUP OF CONTAMINATED BUSINESSES

Prior to May 1997, the Agency had no policy or guidance for making decisions to clean up
businesses contaminated with methyl parathion. Consequently, regions developed
inconsistent policies regarding business cleanups. Region 5 did not clean up businesses
at the first site in Lorain County, Ohio. Region 4 initiated cleanups of 24 businesses,
including restaurants, stores, day care centers, and churches. Region 6 initiated one
business cleanup, then discontinued the practice.

This lack of consistency not only left the Agency vulnerable to criticism, but also
resulted in the use of additional funds and resources for removal actions at sites that
are unlikely to cause continuous exposure to methyl parathion. The funds and resources
could have otherwise been available for removal actions at higher priority sites with
continuous exposure.


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The recently issued OSWER Directive 9285.7-27A, Cleanup of Methyl Parathion Contaminated
Businesses (undated) provides guidance to the regions in making cleanup decisions
regarding businesses contaminated with methyl parathion. The guidance provides that
decisions should be based on the urine protocol criteria, especially those with resident
population or residential type exposure; i.e., nursing homes, day care centers, or
hospitals. Consideration should also be given to the businesses' ability to pay.

RELOCATION COSTS

The Agency was not consistent in its application process for resident relocation

eligibility or subsistence payments made to relocated residents. These inconsistencies

provided the potential for fraudulent and excessive relocation costs. At both the
Jackson

County and New Orleans sites, the Corps, through an interagency agreement with the
Agency,

was responsible for processing applications for resident relocation and making
subsistence

payments. Corps personnel at each site established their own application process, as
well

as the subsistence rates and other types of expenses (i.e., laundry, taxis).

Application Process

The Corps at each site set its own application requirements. The Corps at the Jackson
County site used a detailed application process, including resident identification and
household size verification. The Corps in New Orleans initially required no
identification or verification from its applicants.

The Corps at the Jackson County site, with assistance from Region 4 program officials,

developed draft procedures outlining the application process and eligibility
requirements,

including verification of residency and household size. To substantiate their
eligibility, applicants could submit various documents to verify residency and household


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size, including drivers license, social security number, rental agreements, rent
receipts,

tax returns, proof of public assistance, and/or mail.

The Corps in New Orleans initially did not require any documents to verify residency or
household size. Based on a recommendation made by OIG 01, the Corps subsequently began
requesting social security and drivers license numbers from its applicants. However, the
Corps did not verify household size.

Additionally, 01 suggested other improvements in the application process that would help
the Agency protect itself against abusers and fraudulent claims. The improvements
included:

a certification and false penalties
statement;

a requirement for applicant
identification/verification for release
of subsistence payments;

a medical release form; and

simpler, separately listed questions on the
questionnaire regarding source and
application of methyl parathion.

01 recently learned that Region 5 is currently using contract services to develop its own

application process for use by the Corps at the Chicago site. We understand from 01 that

the proposed application package does not require social security or drivers license

numbers from applicants as recommended by 01 and implemented by the Corps in New Orleans.

The drafting of an additional application package by Region 5 appears to be a duplication

of effort and an unnecessary expenditure of resources. A standard application package
for


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use by all regions could have prevented the inconsistencies and reduced the potential for
fraudulent or excessive claims.

Subsistence Costs

The Corps also independently determined subsistence payments at the Jackson County and
New

Orleans sites. Corps personnel at each site used different approaches for determining
per

diem and lodging rates. The rates varied between sites and were not based on any
specific

standard.

The process followed in Jackson County evolved from the General Services Administration
(GSA)-approved daily subsistence rates to a method which based subsistence payments on
three options. For Option 1, the applicant could elect to stay in government-furnished
apartments, and receive a one-time incidental expense allowance of $200. With Option 2,
the applicant made his or her own arrangements and accepted a fixed amount of money based
on the average daily cost of a one, two, or three bedroom apartment, and a one-time
incidental expense allowance of $200. With Option 3, the applicant made his or her own
arrangements and requested reimbursement on an actual basis, not to exceed a set amount
per day.

The process in New Orleans also evolved from GSA-approved daily subsistence rates.

However, the method of calculation was based on the applicant making his or her own

arrangements and accepting a fixed amount of $15 per day per household, with no
incidental

expense allowance.

Region 5 is currently determining its own method for calculating subsistence payments.


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Overall, insufficient resident verification procedures and variances in subsistence
payments, not only leaves the Agency open to criticism, but also results in inequitable
and potentially fraudulent payments.

DOCUMENTATION OF PERSONAL PROPERTY

We found inconsistencies in the degree of documentation maintained by the regions to
identify personal property items. The regions used various contractors or the Corps to
appraise and document personal property for removal and replacement purposes. Each
servicing agent developed its own documentation requirements for personal property
records.

Draft OSWER Publication 9360.3-18, Guidance on Compensation for Property Loss in Removal

Actions, dated September 1996, outlines the procedures for compensating for property los

due to hazardous substance release or the resulting response effort. The guidance

requires the OSC to record the condition of any property that potentially could be
damaged

during response activities. Documentation must be in writing, and may be supplemented

with photographs and videotapes. This documentation would be used as a basis to
determine

appropriate compensation after the response was complete.

The quality and sufficiency of personal property documentation varied at the different
sites. Personal property records maintained at the New Orleans site included a
combination of detailed videotapes and photographs (also available on CD ROM). They als
included specific property descriptions and detailed appraisals on contaminated
reimbursable items. In contrast, files maintained at the Jackson County site were not a
specific. The files included videotapes and some photographs but included more generic
descriptions and appraisal values for contaminated reimbursable items.

The lack of specific detail could expose the Agency to fraudulent claims and additional

expenses should residents dispute reimbursements and/or claim items as missing or
damaged.


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At the same time, too much documentation could result in unnecessary expenditures that
outweigh the benefit derived.

RESTORATION OF INDIVIDUAL RESIDENCES

Residential restoration at the New Orleans site using Region 6's ERCS contracts proceeded
more timely than restoration at the Jackson County site using Region 4's interagency
agreement with the Corps. For comparative purposes, the latest OERR Methyl Parathion
Response Status report, dated July 25, 1997, stated that of the 430 households requiring
relocation in Mississippi, only 75 cleanup/restorations were completed. Louisiana, with
cleanups initiated approximately 1 month after the start of cleanups in Mississippi,
reported 187 households requiring relocation, with 182 cleanup/restorations completed.

The delays encountered in Jackson County were primarily attributed to the lengthy
procurement process followed by the Corps. Initially, the Corps issued individual
purchase orders for the restoration of each residence. To alleviate the delays and
backlog, the Corps recently issued an indefinite delivery/indefinite quantity contract
which provided for the issuance of work orders to three contractors to cover the
restoration of numerous residences. In the interim, Region 4 also issued work orders
under its ERCS contracts to assist with the restoration work in Jackson County.

Region 5, also proposing to use the Corps for restoration at the Chicago site, has
expressed concerns regarding funding and capacity available under its ERCS contracts
should the Region need to obtain additional restoration support beyond the Corps.

SUMMARY

The lack of clear and concise national guidance resulted in regions developing their own
procedures. Regional responses could have proceeded more efficiently and with less risk
to the government, had the Agency developed clear and concise national guidance.


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SUGGESTIONS

We suggest that the Acting Assistant Administrator for Solid Waste and Emergency

Response:

1.	Modify existing guidance and develop new guidance,
as required, to address emergency removal actions at
methyl parathion sites that at a minimum:

a.	Clarifies important factors related to its
protocol for testing levels of methyl
parathion in residents' urine, including
resources for urine sampling and monitoring,
and disclosure and notification requirements
for resident occupancy changes.

b.	Outlines criteria for business cleanups,
including specific eligible expenditures.

c.	Outlines applicant eligibility procedures,
including verification of residency and
household size, as well as a standard for
computing subsistence payments. The Agency
should consider providing standard
application forms for use by the Corps or
other servicing agents.

d.	Defines a standard for sufficient
documentation of personal property items.

2.	Encourage Region 5 to work with the Office of


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Acquisition Management to explore other contracting
alternatives to obtain services in a timely manner,
if delays are encountered and additional resources
from the ERCS contracts are required.

================================================================ REPORT DISTRIBUTION

REPORT DISTRIBUTION

Office of Inspector General
Headquarters

Inspector General (2410)

Deputy Assistant Inspector General
Deputy Assistant Inspector General
Headquarters Audit Liaison(2421)

Divisional Office

Divisional Inspectors General for Audit

Headquarters Office

Assistant Administrator for Solid Waste and Emergency Response (5101)

Director, Office of Emergency and Remedial Response (5201G)

Deputy Director, Office of Emergency and Remedial Response (5201G)

Audit Liaison, Office of Solid Waste and Emergency Response (5101)

Agency Follow-up Official (2710)

Agency Follow-up Coordinator (2724)

Accountability Staff Director (2724)

Assistant Administrator for Administration and Resources Management (3101)

for Internal Audits (2421)
for External Audits (2421)


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Associate Administrator for Regional Operations and State/Local

Relations (1501)

Associate Administrator for Communications, Education,

and Public Affairs (1701)

Director, Grants Administration Division (3903R)

Director, Office of Policy and Resources Management, (3102)
Director, Office of Acquisition Management (3801R)

Special Assistant to the Deputy Administrator for
Administrative Issues (1103)

Regional Offices

Regional Administrators
Directors, Superfund Division
Audit Follow-up Coordinators

Other

Office of Community Health Services
Mississippi State Department of Health
P.O. Box 1700
Jackson, MS 39215-1700

Mobile District, Corps of Engineers
P.O. Box 2288
Mobile, AL 36628-0001

Pesticide and Environmental Protection
Agriculture and Environmental Services Office
Louisiana Department of Agriculture and Forestry
P.O. Box 3596

Baton Rouge, LA 70821-3596

Real Estate Division


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New Orleans District, Corps of Engineers

P.O. Box 60267

New Orleans, LA 70160-0267

:====================================================== END OF REPORT


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