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June 2008
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Word on the Street
IAQA CHAPTER PURSUES CHARITY OPPORTUNITY
Earlier this
year the Ft. Lauderdale Chapter of the Indoor Air Quality Association
(IAQA) worked with several local businesses to arrange an indoor air
quality assessment on the home of a local family whose 5th grade son
was diagnosed with cancer.
The chapter
networked with other local community leaders and arranged for the
complete assessment at no cost.
Shortly after
the boy’s diagnosis, a medical team instructed the family on the
environmental prerequisites required after his release from the
hospital. The child’s elementary school, seeking information about
indoor air quality testing and air duct cleaning, contacted
Ft.
Lauderdale’s IAQA Chapter
Director, Maurice Baum, who started searching for solutions
immediately.
“Their son’s
unanticipated medical condition has imposed an unexpected and
devastating emotional and fi nancial hardship on this young family”
said Baum. “They are very grateful for the generosity and timeliness
of our local professionals in their time of need.”
The Ft.
Lauderdale Chapter of IAQA recognized COIT Services, Inc.,
Environmental and Analytical Management, Inc., and
Wisconsin Occupational Health for donating their services
to the family.
The Ft.
Lauderdale Chapter of IAQA is still collecting donations from anyone
who wants to help ease the financial burden of this family through
services and/or financial contributions of any amount. To contact the
Ft. Lauderdale Chapter of IAQA, call 877-663-5336 or email
err2003@bellsouth.net.
Ben Auman is
Chapter Relations Director for the Indoor Air Quality Association. He
may be reached at (301) 231-8388, ext 11, or
bauman@iaqa.org.
BBJ ENVIRONMENTAL ACQUIRED
The assets of
BBJ Environmental Solutions, Inc. (BBJ) have been acquired by ACP BBJ,
LLC an affiliate of Miami-based private equity firm Americas Capital
Partners. BBJ manufactures and distributes a range of industry-leading
products used to optimize indoor air quality and the energy efficiency
of commercial air conditioning systems. ACP has appointed Robert G.
Baker as CEO. Mr. Baker is the founder and former Chairman of BBJ.
According to
ACP Senior Vice President David J. Matthes, BBJ came to the attention
of ACP because the firm’s commercial real estate division has been
using BBJ’s products with outstanding results for many years.
“BBJ makes a
great product, our engineers love it. We were delighted
when we got the opportunity to acquire this company” said
Mr. Matthes.
WHAT HAPPENS IN VEGAS
With its
recent certifi cation by the US Green Building Council,
the Palazzo resort in Las Vegas is now considered the largest
“green” building in the world. The $1.9 billion, 3,000-room resort is
more than four times bigger than any LEED-certified building,
according to USGBC, which presented developer Las Vegas Sands Corp.
with a Silver LEED (Leadership in Energy and Environmental Design)
Certificate at an award ceremony this week. LEED certification is an
independent, third-party verification that a building project is
environmentally responsible, energy-efficient, and is a healthy place
to live and work.
Key features
that led to the Palazzo’s certification include:
artificial turf, drip irrigation and moisture sensors in
planted areas, resulting in a plus-75% reduction in
irrigation needs and swimming pools heated with an
expansive solar pool heating system. In the summer, the
excess solar energy not needed for the pools is directed
to the hotel’s hot water system; and air conditioning
controls in guest suites automatically setback by several
degrees when guests are not present and reset to the
desired temperature upon return.
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Children with Asthma Are Vulnerable to Low-Level Pollution, Study Finds
by Tom Scarlett
Children with asthma living in major cities may be particularly
vulnerable to air pollution at levels below current air quality
standards, including poor indoor air quality, according to new
research conducted by the National Institute of Allergy and Infectious
Diseases The study analyzes the short-term effects of outdoor
pollution levels on asthma symptoms and lung function in children.
Using data collected from (NIAID) Inner-City Asthma Study (ICAS),
researchers examined 861 children with persistent asthma, aged 5 to 12
years, living in low-income areas in seven
U.S. inner-city communities:
Boston, the Bronx, Chicago,
Dallas, New York
City, Seattle and Tucson. Over two years, the researchers
regularly monitored the children's asthma symptoms, breathing
function, and school absences, and obtained daily outdoor pollution
measurements from the EPA's Aerometric Information Retrieval System.
Every six months, they tested lung function twice-daily over a
two-week period. They also asked the children's parents for their
observations of their children's symptoms.
Results revealed that children had significantly decreased lung
function following exposure to higher concentrations of the air
pollutants sulfur dioxide, airborne fine particles, and nitrogen
dioxide. Higher nitrogen dioxide levels and higher levels of fine
particles also were associated with school absences related to asthma,
and higher nitrogen dioxide levels were associated with more asthma
symptoms. Because nitrogen dioxide is derived mainly from motor
vehicle exhaust, these data provide evidence that car emissions may be
causing adverse respiratory health effects in these urban children who
have asthma.
Previous studies have documented the adverse respiratory effects of
very high levels of outdoor pollutants. However, this study involves a
larger cohort of inner-city asthmatic children and a more
comprehensive evaluation of respiratory health effects than prior
studies of this type.
The study's authors report that inner-city children with asthma
experience adverse health effects from air pollutants even when air
pollution levels are within the current air quality standards of the
Environmental Protection Agency. These findings raise questions about
the current air quality standards and suggest that part of overall
asthma management for children living in inner cities may need to
include efforts to reduce exposure to air pollutants.
The study was conducted by the Inner City Asthma Study Group
(ICAS). ICAS was started in 1996 to examine environmental
interventions in the management of asthma. During its 12-year history,
ICAS has contributed to the understanding of childhood asthma and ways
to minimize disease consequences.
The study was funded by NIH's National Institute of Allergy and
Infectious Diseases (NIAID), National Institute of Environmental
Health Sciences (NIEHS), and National Center for Research Resources (NCRR); and
by the United States Environmental Protection Agency.
In another asthma-related development, new research suggests that
free radical pollution in the air could be a cause of asthma,
according to Dr. Duanne Sigmund, based at the University of Melbourne
with the ARC Centre of Excellence for Free Radical Chemistry and
Biotechnology.
Sigmund and Dr Uta Wille, both chemists at the
University
of Melbourne, have
discovered that the atmospheric nitrate radical irreversibly damages
amino acids, which are the building blocks for proteins in the human
body. This, they suggest, could be a cause of some respiratory
diseases.
The nitrate radical is formed by two common atmospheric pollutants;
nitrogen dioxide, which itself is emitted from car exhausts, and
ozone, which is an important greenhouse gas that is harmful to humans.
During the day the sun’s UV radiation breaks down the nitrate
radicals, but the concentrations rise as soon as the sun goes down.
"We were very interested to see what these nitrate radicals do to
the human body since we breath them in at night," said Sigmund.
The duo has found that the nitrate radical reacts with amino acids
to form compounds such as beta-nitrate esters, beta-carbonyl, and
aromatic nitro-compounds. Some of these compounds have been associated
with increased immune response in some respiratory diseases, creating
worse symptoms.
"Our results suggest that the nitrate radical could be a real
culprit for respiratory diseases, yet until this study the nitrate
radical has been previously entirely overlooked in regard to causes
for diseases such as asthma," says Sigmund.
The research will be published in the upcoming issue of the U.K.
Royal Society of Chemistry¹s Chemical Communications.
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Court Orders EPA to Rethink Policy on Carbon Monoxide Standards
by Tom Scarlett
A U.S. District Court judge in
San Francisco
has decided that the Environmental Protection Agency violated the
law and must reevaluate its standards relating to human exposure to
carbon monoxide in the air.
The judge found that EPA violated a nondiscretionary duty to take
a fresh look at the standards every five years. He gave the agency a
deadline of May 2011 to come up with the new standards.
An EPA spokeswoman told
Indoor Environment Connections that the agency believes the
judge’s decision is wrong, and that it plans to appeal the case.
The appeal would go to the Ninth Circuit Court of Appeals in
San Francisco, which is known for favoring
claims filed by environmentalists and other liberal advocacy groups.
The petition in this case was filed by four environmental groups.
The decision could ultimately be reviewed by the U.S. Supreme Court.
The 1990 revisions to the Clean Air Act require the agency to
look at pollution limits, known as national ambient air quality
standards, every five years and decide whether revision of the
standards is needed to protect human health.
The EPA last reviewed carbon monoxide standards in 1994 and last
revised the limits in 1971.
The agency admitted that it missed the five-year deadline, but
began a review process last year and proposed to finish the review
by October 2012.
White ruled, however, that it would be feasible for the EPA to
finish the process by May 2011.
Carbon monoxide is created by the burning of fossil fuels in car
engines and industrial plants. It is lethal at high levels and at
lower levels can contribute to cardiovascular, nervous system and
developmental problems.
Representatives of the groups that sued the EPA last year praised
the ruling and urged the EPA to strengthen the standards.
Jeremy Nichols, director of Rocky Mountain Clean Air Action,
said, "Sadly, current health standards allow our children to be
exposed to dangerous levels of carbon monoxide across the country."
Shana Lazerow, a lawyer with Oakland-based Communities for a
Better Environment, said, "Poor people and people of color suffer
most from carbon monoxide, which is spewed by the refineries and
power plants located in our communities, as well as the congested
highways in our backyards."
Other groups participating in the lawsuit were the
Coalition for a Safe Environment and Physicians for Social
Responsibility.
In addition to setting a final deadline of May 2011, White ruled
he has the authority to require interim deadlines in the review
process.
He ordered the EPA to come with a proposed schedule of interim
steps by July 7.
The judge wrote, "Given how many years have passed since the
EPA's mandatory deadline has expired, the court is wary of merely
providing the EPA a long-term deadline without any oversight or
review."
The current primary ambient air standards for human exposure to
carbon monoxide are an eight-hour average of nine parts per million
and a one-hour average of 35 parts per million.
Communities for a Better Environmental said recent research
studies have shown that exposure of fetuses to carbon monoxide
levels as low as 1.4 parts per million over three months is linked
to low birth weight, which in turn can lead to developmental
problems.
The current national standard was set in 1971. Federal
law requires a reassessment every five years, but the EPA
last reviewed the standard in 1994 and made no changes,
said Lazerow.
Environmental groups in the lawsuit cited two reports
in the journal Environmental Health Perspectives, published in 2001 and 2005, both
found low birth weights among children born to women who were
exposed to carbon monoxide at levels far below those allowed by the
1971 standard.
The EPA says it has come up with a new approach to clean-air
regulation that will streamline the process while incorporating the
latest scientific information. But White, in his ruling, noted that
the agency's own advisory panel of independent scientists called the
new procedures "entirely unsuitable" in January, saying they failed
to provide timely information about the contents of proposed
regulations.
The decision comes at a time of increasing
litigation against builders, landlords and others with claims
relating to carbon monoxide exposure.
Eight lawsuits have been filed against
companies involved with the heating system that malfunctioned at the
Redstone Apartment complex near the University of Vermont in 2005, killing one person and
sickening others.
The lawsuits targeted as many as 10 companies,
including the maker of a pipe that malfunctioned, the
manufacturer of the apartment complex's heating boiler,
the landlord and firms involved in the construction of the
building, its heating system and the natural gas used to
fuel it.
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What Should You Do On An IAQ Investigation?
When asked to write on the above topic, I realized that I could go
off on many tangents.
Many of these directions are the subject of vigorous debate within
the industry. At this
point, there appears to be little agreement on many of these issues.
Witness the difficulty IESO is having arriving at a workable
Assessment Standard.
So, I am writing this article from the basis of “my opinion”.
The value of which I will clarify with a quote from my old
red-neck Uncle Jim:
“Opinions are like back-sides, we all have one.”
I have always attempted to use the concepts of “best industry
practices” or “standards of care”, and “best available science” in
performing my inspections, writing remediation protocols, and giving
advice. But, with the
differences of opinion in our industry, what are “best industry
practices”?
My practice as an IAQ Consultant as evolved over the years and I
find myself involved more and more in litigation support (See the
April 2008 issue of IE
Connections). This
has recently led me to a concept that has impacted every area of my
practice:
“Creating
a legally defensible position”.
The concept is simple, but far reaching.
It encompasses every aspect of business.
The question is simple:
Am I creating a legally defensible position for me, for my
Company, and for my Client?
If yes, go forward.
If no, stop and re-think my approach.
I go forward only with a legally defensible position.
I had a very good Attorney tell me very early in my business career
that contract law was simple:
“Say what you are going to do; and more importantly what you
are not going to do.
Then, for God’s Sake, DO what you said you were going to do; and
DON’T DO what you said you weren’t going to do!
If you follow those principals, how can you have created
damages for someone to win a lawsuit against you?”
For the IAQ Consultant, the process of creating a legally defensible
position starts by defining the scope of work for our services;
which begins with the initial Client Interview, often started over
the phone and completed at the first meeting.
What does the Client want?
Why do they want it?
What is their situation?
Who is involved?
What is their budget? Is
what is requested and what is actually needed?
Are other experts needed for the project?
Can I actually do what is requested?
These are important questions that must be answered in
detail, often with follow-up questions needed to get the necessary
detail. And sometimes,
you just have to walk away!
Let’s look at a couple of case studies and see how this concept of a
legally defensible scope of work can be developed:
CASE STUDY 1:
Potential Client (PC):
“Do you do mold testing?”
Frank Dean (FD): “Yes,
why do you want mold testing?”
PC: “I’m on the
Cleveland Clinic’s lung transplant list and my Doctor wants to know
if my house is contributing to my lung condition.”
(Medical Condition, will have to sample for viable mold and
bacteria, not just spore traps.)
FD: “How long have you
lived in the house?”
(Check for possible lawsuit against previous Owner or Builder.)
PC: “About six years.”
(OK, probably no lawsuit.)
FD: “When did your lung
condition begin, or when did you start to notice symptoms?”
(Looking for some event that might be significant.)
OUTCOME: I found, date
coincident with the start of her illness, that they had replaced he
furnace. No one had told
them that the humidifier on the furnace needed to be periodically
cleaned, as it could be a breeding ground for mold and bacteria.
Also, they kept the old A-coil, now covered with six years of
mold and bacterial growth.
Additional reservoirs of mold growth were found in both
bathrooms. Mold and
bacteria were found to be blowing back into the laundry room from a
blocked dryer vent.
Several deposits of guano were found in the attic surrounding bird’s
nests. I wrote a
remediation protocol reflecting the above.
The house was successfully remediated by a remediation
contractor. A PRV
inspection and sample set showed the areas had been successfully
remediated.
Potentials for disaster:
You just do the requested mold sampling and don’t do a thorough
inspection to find the other reservoirs of contamination.
The lady gets really sick.
They bring in another IAQ Consultant who finds the all the
reservoirs of microbial contamination that you didn’t find.
Have you created a legally defensible position?
CASE STUDY 2:
PC: “Do you do
mold testing?”
FD: “Yes, why do you
want mold testing?”
PC: “We just bought a
house from that #@%&#!* Builder and the finished basement leaked
during the last rain and there is Black Mold all over the drywall,
and they don’t want to fix anything.”
(Probable lawsuit!)
FD: “Who is the
Builder.”
PC: “It’s that no good
#@%*@%&# XYZ Building Co.”
FD: “Well, I’m on
retainer with the XYZ Building Co. and I’m afraid that I cannot
offer you further advice.”
OUTCOME: I called the
Divisional President of the XYZ Building Co. and told him about the
call. He overrode the
Service Department and ordered that they fix the problem quickly.
Lawsuit avoided.
Potentials for Disaster:
You don’t find out who the Builder is before you take on the
project. Now you have a
definite conflict of interest, and will probably lose the Builder as
a Client. Because you
have an agreement with the Builder, it is possible that your report
for the Homeowner will not be admissible and the Homeowner might be
very upset. Have you
created a legally defensible position?
CASE STUDY3:
PC: “Do you do
mold testing?”
FD: “Yes, why do you
want mold testing?”
PC: “I bought a
condo from ABC Builders and we have numerous defects that have not
been satisfactorily repaired under warranty, and now my wife and two
year old son are noticing health symptoms.
We want to find out if these defects have caused mold to grow
and cause our health issues.
(Probable lawsuit.
Wants determination that mold is in the building[OK, I can do
that.], and that mold is causing the adverse health symptoms [Oh
Darn, I can’t do that!
In a case decided last fall, the Ohio’s Supreme Court decided that
only a Medical Doctor can determine or comment upon medial
causality. Not being a
MD, I cannot comment on health issues!])
FD: “ABC Builders is not
a Client, so I can do the investigation and sampling that you are
requesting. But, you
will need a Medical Doctor to comment upon the health issues.
Do you have a good Medical Doctor?
And, have you retained an Attorney?
PC: “Yes, our allergist
is Dr. Suzie Smith, and our attorney is Mr. John Howe, with the
firm: Dewey, Cheetam and Howe.
FD: “May I have your
permission to contact Mr. Howe and discuss the particulars of the
case.”
PC: “Yes, I will call
him and let him know it’s OK to discuss the case with you.”
OUTCOME: I did a
thorough investigation of the condo and found several construction
defects that caused water intrusion and mold growth.
This mold growth was documented with air and surface samples
(spore tramps and viables).
The Client’s Allergist said that it was highly probable that
the mold caused the wife and small boy’s symptoms because they were
allergic to several of the mold species found in the condo and the
onset of their symptoms correlated with their move to the condo.
ABC Builders decided that it was to their advantage to settle
the case and they bought back the condo.
Potentials for Disaster:
You do an inadequate sample set (in this case, no viables) and the
MD doesn’t have the data she needs to determine causality.
Or, you are a “One-Day-Wonder”, someone who has taken a one
day mold class and passes himself off as a mold expert, and you then
you can’t pass muster as an expert witness (the Daubert challenge),
so all of your data is inadmissible as evidence in Court.
Mr. Howe would not be pleased as he now has no case.
Have you created a legally defensible position?
I have only presented three case studies to this point, but the
possibilities for problems are endless.
I hope that you see other pitfalls in not completely
determining and communicating your scope of work and knowing all of
the parties involved before you take on the project.
All of the calls started with the same question, but went in
totally different directions.
As part of your scope of work, you will have to decide:
“To sample, or not to sample?
That is the question.”
There seems to be a vigorous debate on the subject.
For me, it is simple.
The question is:
“How do you document that there is, or in the case of the PRV is
not, mold present unless you test?”
Without documentation, you do not have a legally defensible
position.
But, any sampling protocol must be based on a sound
hypothesis. What are you
trying to find out? What
are you trying to prove?
This development of a sound sampling hypothesis and the resultant
sampling protocol has been the subject of several articles in
IE Connections by Dr.
Harriet Burge, and others.
Find them and read them.
If you cannot state your sampling hypothesis clearly, so that
any Jury can understand it, you are not operating from the point of
good science, and do not have a legally defensible position.
CASE STUDY4:
PC: “Hi Frank, I
need to have some mold sampling done.”
FD: “Why don’t you do it
yourself?” (The caller
is a friend who is the Safety and Hazardous Materials Officer for a
large hospital in a nearby city.)
PC: “Can’t, I’ve got an
employee complaining about his mold allergies.
It happened right after he got transferred into an office he
doesn’t like. He has
written a complaint to OSHA with a letter from a Doctor, and I need
an outside consultant to run the tests to avoid a conflict of
interest. I figure we
will need 5 or 6 spore traps and 5 or 6 viables.
FD: “What did the Doctor
say about his allergies?”
PC: “Doctor said the guy
was allergic to Alternaria.”
FD: “Great, Alternaria
has a large, distinct spore.
We don’t need the viable samples to make the case.
It will cost you a lot less.”
OUTCOME: I took spore
traps at the guy’s desk, in the adjoining offices on both sides, in
the hallway outside his office, and outside the building for
control. There was no
Alternaria in any of the samples.
The complaint and complainer went away.
Potentials for Disaster:
Limited, because the Client was a friend.
But, because I saved her Hospital money, I’ll be first on her
list to call in the future.
CASE STUDY 5:
Last year I developed and taught a mold class for a large
corporate relocation company.
At one office, they told the story of a Seller who had mold
problem. He called his
friend, an Industrial Hygienist, who advised him that since the US
EPA and New York City Guidelines both assess a project by square
feet of visible mold, he should make sure that there was no
mold visible. Then, when
there is no visible mold, the Seller should call in the IH
and he, the IH, would write a letter stating that on his inspection
he saw no visible mold.
The relocation company used this report provided by the
Seller, prepared by his friend, the IH, saying that there was no
visible mold. The
relocation company bought the house for $240,000.00.
OUTCOME: The corporate
relocation company now owned the house.
A prospective Buyer hired an IAQ Consultant run air samples.
There were very high levels of airborne mold in the
house. Further
evaluation found mold growth on the back of almost all of the
basement drywall, and in two bathrooms.
Total costs to remediate, rebuild, hold and re-sell the house
exceeded $160,000.00.
The relocation company now requires air samples for all the houses
it buys.
Potentials for Disaster:
You did a visual inspection for the relocation company and took no
samples. The company
later finds a mold problem.
Their attorney calls you.
Do you have a legally defensible position?
Now, there may be some of you who have read to this point
who are thinking it’s not like that out there.
What’s with all this focus on Law, we are not Lawyers.
We are IAQ Consultants.
Let me suggest that you might be more naive than you need to
be.
To some Attorneys, hopefully a minority, the practice of
law is “blood sport”. To them,
the concept of fairness, morality, right and wrong are secondary to
winning the case. Some
Attorney’s will do whatever it takes to win for their Client.
Since we never know when our reports will end up in Court;
all of our reports should be written as though they will
end up in Court.
This means that our inspections, any sample sets, and the
report itself must be able to stand up to the highest levels of
scientific and legal scrutiny.
You must realize that a good Attorney will get an independent
IAQ Consultant to go over your report line by line, looking for
ammunition to discredit you and your report.
I have been on both sides of this process, and it is not
pleasant! (Although, I
must admit to getting some perverse pleasure from destroying a Home
Inspector that has taken a one day sampling class who then does an
inadequate, minimal sample set and doesn’t know why he has taken the
samples or what the lab report means.)
Why did you do what you did?
What was your hypothesis for your inspection, and
your sample set?
Are they scientifically valid?
Are they responsive to what your Client needs and
wants? Is your
report “bulletproof”?
If you cannot answer these questions; have you
created a legally defensible position?
BIO: Frank B. Dean, CIE,
is an IAQ consultant based in Columbus, Ohio, doing IAQ assessments,
training, consulting and litigation support throughout the Midwest.
His company, The PDF Group, LLC is an approved course
provider for the IAQA.
Mr. Dean has spoken on IAQ issues nationally, including at the IAQA
convention. He is a
frequent contributor to IE
Connections.
He can be reached by phone at:
614-846-7100, or by email at:
pdfgrp@earthlink.net
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What does it mean when I have high levels of basidiospores indoors?
Basidiospores are produced by all fungi in the
class basidiomycetes.
The spores are the result of sexual reproduction, and are produced
on small pegs on the surface of a club-shaped cell called a basidium.
The pegs are called sterigmata, which, in many cases, are
specially designed to forcibly shoot the spore into the air.
The spores that are released in this way are bilaterally
symmetric (instead of being radially symmetric as are most other
kinds of spores).
Because of this bilateral symmetry we can recognize basidiospores as
a class under the microscope.
Remember, however, that basidiospores that are not forcibly
discharged do not have this distinctive shape, and generally are not
recognized. Fortunately,
few if any of these are important in indoor air.
Basidiospores are abundant in outdoor
air and are released from Basidiomycetes such as
mushrooms, puffballs, shelf fungi, and others that produce
large fruiting bodies.
Rusts and smuts also produce basidiospores.
In these groups, the basidiospores are very small,
colorless, and thin-walled, and are easily missed on air
samples.
Finally, there is a third group of fungi that produce
basidiospores: the basidiomycetous yeasts.
These include the very common yeasts
Sporobolomyces
and Rhodotorula.
As with the rusts and smuts, yeast basidiospores
are small, colorless and thin-walled.
Now to the real question:
Do any of these fungi grow indoors?
The answer is “yes” and, in fact, some are
relatively common indoors.
The most common are the basidiomycetous yeasts.
Both grow in wet places such as humidifiers, drip
pans where water is cool, and continuously wet materials.
I have seen
Sporobolomyces basidiospores as the most abundant
spore type in a building, with concentrations exceeding
10,000/m3 of air using cultural sampling.
Actual spore concentrations were probably much
higher.
Another group of Basidiomycetes that grows indoors is the
wood rotting fungi such as
Serpula and
Poria. These are in the
same group as the “shelf” fungi that you see on trees in
the woods.
Serpula produces
brown curtain-like fruiting bodies, while
Poria produces a
thin white fruiting body that looks somewhat like paint.
Both of these fungi produce distinctive spores that
could be identified specifically by a well-trained
analyst.
Finally, in really wet environments such as might occur
following a severe flood mushrooms may grow into the
occupied space.
I have seen rows of mushrooms growing out of the
baseboard in flooded buildings in Michigan.
How do I interpret the data for “basidiospores” on a
report? Most
basidiospores do occur only outdoors, and if they are
found indoors they have usually penetrated from outdoors.
Generally indoor concentrations of these outdoor
spores are lowest indoors.
If they are higher indoors, it may be that outdoor
concentrations were much higher hours before you collected
your samples. If
indoor basidiospores concentrations are much higher
indoors than out then it is worthwhile looking for a
source. Also, if
the analyst has noted on the report that the indoor
basidiospores were all alike while the outdoor aerosol had
the typical mixture, then it would certainly be worthwhile
investigating the possibility of indoor growth.
If this is not
noted on the report, then it might be worthwhile to call
the lab and ask the analyst to go back and look again.
We have been doing some research on how to improve
reporting of basidiospores to solve some of these
interpretation problems.
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How to Handle a Sewage Contamination Disaster
This case study discusses a 3,400 square foot-
condominium unit that became contaminated with sewage, the challenges
that were posed, the testing methods used to determine effectiveness
of remediation, and some unusual remediation methods that were
eventually required.
Building
and damage
The penthouse unit has three bedrooms and four
bathrooms, and is located on the 20th floor of a
Florida
Gulf Coast
complex built in 2002. The present owners purchased the unit in
December of ‘04. Extensive
remodeling began in April of ‘05 and was completed in March of ‘06.
In all four bathrooms the new finish floor was
travertine tile installed over the original ceramic tile.
The various layers of flooring materials in the bathrooms at
this point consisted of:
o
Concrete slab
o
Adhesive
o
Cork
o
Thin set
o
Original ceramic tile
o
Cement board
o
Adhesive
o
Cork
o
Thin set
o
Travertine tiles.
By the time construction was completed, the new
bathroom floors were elevated well above the original floor and flange
connection to the commode drain lines.
Commodes were installed in September
of 2005 and were in use from then until the discovery of
the leaks.
The family moved in during March of 2006.
On May 13th, they noticed wet drywall behind the
commode in the master bathroom.
A plumber investigated, looking first for
plumbing leaks in the wall.
None were found. On detaching the commode, he found multiple
stacked extenders had been used to compensate for the added floor
height, rather than extending the drain line.
This assembly had been leaking for
some time, probably since installation, as completely
saturated flooring materials were found. The same
condition was eventually determined to affect all four
commodes.
Contamination
Commode installations had leaked at their
connection to the flange.
Each time a commode flushed, contaminated water seeped out and began
spreading on top of the concrete subfloor, under the multiple layers
of flooring materials. By the time of discovery, “black water” had
directly affected an irregular area of 100 to 250 square feet around
each of the four commodes.
When water penetrated under walls
into adjacent areas, contamination wicked up into wall
materials and also affected the black walnut hardwood
strip flooring in the rest of the unit. This flooring had
also been installed over previous materials, resulting
again in multiple layers of flooring being affected.
Sewage composition
A wide variety of organisms are found
in sewage. Some are
human pathogens. Many pathogens may be present, including
bacteria (Salmonella, Shigella, Staphyloccocus), protozoa
(Giardia, Entamoeba), parasites (worms and flukes), and
viruses (norovirus, echoviruses).
Sewage pathogens vary in their characteristics,
including resistance to desiccation, to changes in
temperature or pH, and to contact with biocides.
After leaving the digestive tract, some die
quickly. Others may be able to survive for weeks or even
years in the right conditions.
Investigation
IET was retained to develop a scope of work and
protocol for the necessary remediation. A primary concern of the
homeowners was that they didn’t want to cover up still-contaminated
materials when new materials were installed. They insisted on thorough
documentation of return to sanitary conditions before reconstruction.
Various parties had input into the project, which
led to IET performing several inspections to address different issues
between June and December of 2006.
Sewage screen testing indicated the presence of
indicator organisms (see discussion of sewage remediation testing
below) on various materials, including concrete slab subfloors, in all
the areas where flooring showed elevated moisture content. Finish
flooring, hardwood and travertine, as well as the various layers
beneath, had to be removed in order to access and decontaminate the
concrete slab subfloor, while using appropriate precautions to prevent
the spread of contaminants and to protect worker health. Wall
materials were contaminated by sewage in some areas, and extensive
mold growth not discussed in this article, were also issues.
IET developed a written protocol for the work and
an experienced local mold remediation contractor was retained to do
the work.
Remediation
To prevent cross-contamination of unaffected
areas, containment was erected and negative pressure generated in the
work zones. Any wall or flooring materials indicating elevated
moisture content were removed down to the studs or concrete slab,
which was then cleaned and treated with an EPA-registered biocide.
All surfaces inside the containments were thoroughly cleaned
and treated with biocide.
IET was then contacted to perform a
post-remediation evaluation.
Sewage
remediation testing methods
As noted above, many pathogens can be present in
sewage. For a number of
reasons, testing for all of them is impractical:
o
Many of the pathogens may be present in
low concentration. However, it may require only a few to cause
disease.
o
The statistical likelihood of detecting
a low concentration of a pathogen in a sample from a small area is
low.
o
Testing methods for particular
pathogens may detect only one or a few pathogen types. Testing for all
potential pathogens would require many tests, at high expense, even
assuming tests were available for all of them.
For these reasons and others, sewage remediation
testing is usually done by testing for "indicator organisms,” easily
detectable bacteria usually found in a sewage-contaminated
environment. While some bacteria in an indicator organism group may be
pathogenic, indicator organisms are also used to extrapolate whether
other less easily detected pathogenic organisms are present.
In other words, testing is done to determine the
level of cleanliness or sanitation. If indicator organisms are absent
or are present at very low levels, we assume the level of sanitation
is adequate. Typically, IET uses total and/or fecal coliform bacteria
and Escherichia coli (E.
coli) as indicator organisms.
Proper sewage remediation methods
rely primarily on aggressive cleaning to physically remove
contaminants, rather than on the use of biocides to kill
pathogens. One
reason is that Gram-negative bacteria, very common in
sewage-contaminated environments, may release endotoxins
when they die, with potentially serious human health
effects. Physically removing bacteria by thorough cleaning
helps prevent release of endotoxins.
Nevertheless, biocides are extremely
useful in sewage remediation, especially those biocides
which provide both cleaning and biocidal capabilities.
Coliform bacteria
Coliform bacteria are often used as
indicator organisms. A number of genera make up this group
of rod-shaped, Gram-negative, non-spore forming bacteria.
They include many human pathogens, as well as bacteria
that form a normal part of a healthy intestinal flora and
bacteria found in the general environment. The
presence of
coliform bacteria should not be considered a direct
indicator of sewage contamination. However, the
absence of
coliforms on a surface that was previously contaminated
with fecal material is an excellent indication that
remediation has been effective and that a sanitary
environment has been re-established at the point sampled.
Fecal coliforms
This subgroup of coliform bacteria is
more directly associated with fecal contamination and is
also used as an indicator organism for sewage
contamination.
Escherichia coli: E. coli
is one species of the coliform group and is another indicator organism
IET uses when testing for sewage contamination.
It is found primarily in the intestinal tracts of mammals and
on surfaces contaminated with feces.
E. coli can sometimes
survive outside the body for extended periods. Most strains of
E. coli are not pathogenic
and indeed form a normal part of human intestinal flora.
E. coli can even be
beneficial to human health by producing vitamin K and limiting the
establishment of pathogenic bacteria.
When testing for residual contamination after
sewage remediation, the presence of
E. coli is considered a
direct indication of human fecal contamination, although there are
other potential sources.
Screening
vs. quantitative analysis
Most of the time, IET uses a “Coliform and
E.coli screen.” This qualitative analysis determines the presence or
absence of E. coli and of
total coliform bacteria.
It provides no data about how many of these organisms were present.
This means it is possible for a quantity slightly above the lower
detection limit, an amount that doesn’t necessarily indicate a
significantly contaminated environment, to generate what is in effect
a false positive.
A quantitative “Sewage
Assessment/Clearance” analysis provides more information
and is usually used for the final post-remediation
evaluation. It may quantify total coliforms, fecal
coliforms and E. coli, allowing the consultant to make decisions about whether the
numbers found indicate a contaminated surface or environment.
Results of
post-remediation evaluation (PRE) and follow-up work
After about two months of remediation work in
early 2007, which addressed mold remediation as well as sewage
contamination, remediators contacted IET to perform a post-remediation
evaluation.
February 27 (PRE) inspection:
Mold remediation was successful.
Sewage remediation testing, using screening methods, showed
that remediation had been successful in some areas, but not in others.
IET made suggestions to the remediators on appropriate
remediation methods and additional work was completed.
March 15 (PRE) inspection:
Sewage remediation testing, using screening
methods, found that remediation had been effective in some
more areas, but other areas were still contaminated. IET
again discussed appropriate remediation methods with the
remediators and additional work was done.
April 02 (PRE) inspection:
Sewage remediation testing, using screening
(presence/absence) methods indicated successful
remediation in additional areas, but other samples still
showed contamination.
After discussion with the owners, it was decided to
use quantitative analysis in case the qualitative
screening was producing what “false positives” by showing
the presence of coliforms when they were present only at
very low levels.
April 05 (PRE) inspection:
Quantitative analysis using the Sewage Assessment
and Clearance method found fecal coliform bacteria in
significant quantity in some samples.
We were not expecting these results,
especially considering the extended time, about 9 months,
since additional contamination had stopped. Previous
sewage remediation projects had been successfully
remediated using the techniques specified. One possible
explanation is that micro-organisms had been able to form
biofilms, complex microbial communities attached to a surface and
encased in a slime matrix. Microbes in a biofilm may be much more
resistant to desiccation, to mechanical disruption, and to detergents
and biocides.
As repeated attempts to decontaminate
surfaces had not been fully effective, IET decided to
directly supervise further remediation work. The
remediation contractor provided workers and equipment, and
IET located specialized equipment for use on a rental
basis.
Remediation
processes used
1.
Thorough cleaning: IET used a large rotary scrubber
with a stiff bristle brush to scrub the concrete
aggressively.
The solution used was a quaternary ammonium based
cleaner/disinfectant. It was not EPA-registered for sewage
remediation and was used primarily for its cleaning
potential. Any
biocidal effect was a welcome bonus.
Rationale: Previous cleaning attempts
may not have been aggressive enough to disrupt possible biofilms. The porous
surface of concrete, as well as paint and adhesive residues, provide
crevices in which bacteria can “hide,” and into which biocides and
cleaners may not be able to penetrate effectively. Aggressive cleaning
methods might be more effective at disrupting biofilms, dislodging
sewage organisms and/or encouraging penetration of biocides into
pores.
2.
Through rinsing and extracting: IET used a
high-pressure washing/extraction system designed for
cleaning floor tile.
900 psi rotary spray jets “flushed” contaminants
out of pores. The spray jets were enclosed in a vacuum
hood, so there was no overspray with its potential to
aerosolize contaminants.
Soils and contaminants were collected by the vacuum
system before they could sink back into the concrete
pores. To prevent aerosolization of contaminants, vacuums
exhausted to the exterior.
Dehumidification controlled humidity.
Rationale:
Effectively removing suspended soils and contaminants from a
porous surface is difficult, since after being suspended in a cleaning
solution soils often redeposit before they can be extracted or
absorbed.
Normally, a tool of this type connects to a
truck-mounted carpet cleaning machine providing high heat, water
pressure and vacuum. This
was impractical for this project, located on the 20th
floor. IET rented a
portable extraction machine capable of operating the equipment.
3.
True steam cleaning: After
rotary extraction, the surface of the floor was allowed to dry, and
then a rented “true steam” cleaning machine was used.
This professional unit generates a significant volume of steam
at 350°F. Steam is even more effective at penetrating surface pores of
concrete than high-pressure rotary extraction and may also have direct
biocidal effects.
Micro-fiber towels over the steam jets absorbed soils released from
the surface.
4.
Application of disinfectant solution:
IET used a phenolic-based product EPA-registered
for sewage remediation. The product was applied in
compliance with label instructions and allowed to dry for
several hours.
Sample results showed that all areas sampled were
below the lower detection limit of the analysis.
IER was able to contact the owners and inform them
that the environment had now tested as sanitary and that
reconstruction could begin.
Lessons learned
When a concrete slab has been soaking in sewage
for weeks or months, thorough cleaning and sanitation can be
challenging. It is possible that biofilms can form and significantly
increase resistance to desiccation, detergents and biocides.
Aggressive cleaning, including the
use of efficient methods for removing suspended soils and
contaminants before they redeposit, is essential.
Aggressive remediation using methods such as those
described, even when rental of specialty equipment is
required, is likely to be a good deal more cost-effective
than repetitive ineffective remediation attempts combined
with repeated sampling.
Mold remediation is usually done
under conditions that are as “dry” as possible to help
prevent further amplification.
This approach may be counter-productive in sewage
remediation, for which aggressive cleaning methods with
large volumes of water may be more effective.
The remediator’s challenge is to use enough water
for effective cleaning while still controlling it well
enough to prevent wetting of adjacent materials or the
development of excessive humidity.
Timothy D. Toburen is an Indoor Environmental Consultant
for Indoor Environmental Technologies, based in
Clearwater,
Florida.
He has worked in the restoration, remediation and
environmental consulting industries for over 35 years,
serving on the committees that produced both the IICRC
S520-2003 Mold Remediation and S500-2006 Water Damage
Restoration standards.
He can be reached by e-mail at
ttoburen@ietbuildinghealth.com or by phone at (727)
446-7717.
Will Spates is President of Indoor Environmental
Technologies, based in Clearwater, Florida.
He has over 20 years of experience in the environmental
consulting industry. He can be reached by e-mail at
wspates@ietbuildinghealth.com or by phone at (727)
446-7717.
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