HomeMy WebLinkAboutStructural Condition and Mold Survey for Augusta Joint Law Enforcement Center
Augusta Richmond GA
DOCUMENT NAME: ST~UC.ltJc<,AL ~Ol"'D\,TIDN A.tV'\) mOL\) SlJR.V6'1
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DOCUMENT TYPE:
YEAR: ;;Z 00 L\
BOX NUMBER: ?. ~
FILE NUMBER: ) 'l 'Lo y lp
NUMBER OF PAGES:
50
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STRUCTURAL CONDITION AND MOLD SURVEY
For
AUGUSTA JOINT LAW ENFORCEMENT
CENTER
401 WALTON WAY
AUGUSTA, GEORGIA
Prepared for
The Augusta Commission
Augusta, Georgia
Prepared by
Cranston, Robertson & Whitehurst, P.C.
ENGINEERS & PLANNERS - SURVEYORS
P.O. Box 2546 & 452 Ellis Street
Augusta, Georgia 30903
September 21 2004
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STRUCTURAL CONDITION AND MOLD SURVEY
For
AUGUST A JOINT LAW ENFORCEMENT
CENTER
401 WALTON WAY
AUGUSTA, GEORGIA
Prepared for
The Augusta Commission
Augusta, Georgia
Cranston, Robertson & Whitehurst, P.C.
ENGINEERS -PLANNERS -SURVEYORS
452 Ellis Street & P.O. Box 2546
Augusta, Georgia 30903
September 21, 2004
Revised October 13, 2004
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T ABLE OF CONTENTS
Pae:e Number
EXECUTIVE SUMM.ARY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 1
GENERAL .................................................................. 3
DISCUSSION ................................................................ 3
Building Structure Survey ............................................... 3
Mold Survey ........................................................... 4
CONCLUSIONS ......... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8
RECOMMENDED CORRECTIVE ACTION ...................................... 8
APPENDICES
Appendix A -
Appendix B -
Sampling Location Plans
Limited Indoor Air Quality Investigation
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EXECUTIVE SUMMARY
This report has been prepared for the Augusta Commission for the purpose of evaluating
the structural integrity and mold in the Augusta Joint Law Enforcement Center located at 401
Walton Way in Augusta, Georgia. The building construction was completed in 1985. Since the
construction was completed, various problems have occurred including roof, wall, and window
leaks. The study primarily focused on the administrative areas as well as the detention tower.
This report presents an initial observation of the building structure and the results of mold
testing. It is intended to provide an opinion of the structural integrity of the building structure
and to determine if mold spores discovered inside the building present elevated health risks when
compared to mold naturally occurring outside. This report only addresses the structural integrity
of the building and mold testing and does not include architectural and plumbing fIxtures, or
electrical, mechanical, and plumbing issues.
We have determined that the building structural components are safe in accordance with
the 1985 Standard Building Code. A copy of the design code for this project, the 1982 Standard
Building Code, could not be obtained during the course of this evaluation. However, the
structure was evaluated by using the 1985 Standard Building Code. In general, later editions of
the Building Codes are usually more conservative.
The building frame consists of a concrete column and beam system with a concrete pan
and joist floor system. Minor cracks were observed on the underside of some of the floor panels.
The cracks appear to be non-structural and do not indicate structural concerns at this time. The
exterior walls are formed of 20 gauge metal stud curtain walls which connect to the building
frame. The curtain walls were checked for structural strength and deflection and found to
conform to the 1985 Standard Building Code. During our examination of the exterior surfaces of
the building, we observed that the Exterior Insulation and Finish System panels were not fully
connected to the curtain wall. The exterior panels were warped or bowed out at many locations
and could be pushed inward indicating the failure of some of the connections. This concern is
non-structural but could allow moisture to enter the wall cavity and cause corrosion of the steel
curtain wall system. Corrosion was visible on some of the lower curtain wall connections.
Thirteen (13) tape lift and swab tests and nineteen (19) air tests were performed by an
Augusta environmental fIrm, Alternative Construction & Environmental Solutions, Inc., at the
facility. The test results indicated that approximately 17 different types of mold spores are
present in the building. Ten (10) of the mold spore types were identifIed outside. In most cases,
the mold spore comparisons of the inside and outside of the building were approximately equal.
The penicillium mold spore counts were much higher inside of the buildings when compared to
the outside air test. Based on this testing, we have determined that the elevated mold levels
inside the building are signifIcant and could possibly present an increased health risk to
individuals who may currently suffer with allergies or other respiratory health problems.
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The detention tower was tested on all four levels and found to have mold spore counts
less than the outside air. We have therefore concluded that the mold spore counts in the
detention tower are normal and should not be considered to be a problem at this time.
The corrective action recommended in this report includes removing the source of the moisture,
repairing the damaged Exterior Insulation and Finish System (E.I.F.S) and curtain wall studs, and
then chemically removing the mold from the building by using proper cleaning methods and
procedures. Furthermore, the facility should be retested following the execution of the
recommended repairs and improvements.
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GENERAL
Recently, after opening a section of the northern exterior wall of the Augusta Joint Law
Enforcement Center, representatives from the City of Augusta discovered corroded light gauge
steel curtain wall studs at the first level slab connection. Furthermore, mold was also observed in
the wall cavity at the same location. Concerned with the structural integrity of the facility as well
as the significance of the mold discovery, The Augusta Commission authorized Cranston,
Robertson & Whitehurst, P.c. to conduct a structural evaluation and mold survey of the Augusta
Joint Law Enforcement Center located at 401 Walton Way in Augusta, Georgia. This report has
been prepared for the purpose of performing a limited structural analysis and mold survey of the
facility.
The Augusta Joint Law Enforcement Center is comprised of four (4) primary building
areas. These structures include a two level administration building housing offices and
courtrooms, a three level building housing the Sheriffs Department, a four-level detention tower
above the Sheriffs Department Building, and a separate mechanical building on the opposite
. side of the vehicle sally port from the Sheriff s Department.
This report presents our findings and recommended corrective action based on a visual
observation of the building, review of the structural plans, and physical testing of the facility. A
visual observation may be defined as an examination of the structural elements of the building
that are accessible and in clear view to the naked eye at the time of the observation. Portions of
the building surfaces were not removed to further evaluate specific framing and foundation
elements of concern. This report only addresses the structural integrity of the building and the
evaluation of mold and does not include architectural and plumbing fixtures, or electrical,
mechanical, and plumbing issues.
DISCUSSION
Building Structure Survey:
The facility consists of a primary front public building which houses courtrooms, offices,
records storage, and conference rooms. The Sheriff s Office Building houses training rooms,
photo and crime laboratories, offices, armory, evidence room, and records offices. The detention
tower includes 4 primary floor levels, each with two levels of detention cells. The detention
tower is considered as the 3rd, 4th, 5th, and 6th floor above the Sheriffs Office Building. A
mechanical building is located to the north of the sally port behind the Sheriffs Office Building.
This report addresses only the structure of the two office and courtroom buildings and the
detention tower and does not include the mechanical building.
The building frame consists of a concrete column and beam system with a concrete pan
and joist floor system. Minor cracks were observed on the underside of some of the floor pan
sections. The cracks appear to be non-structural and do not indicate structural defects at this
time. Some of the cracks were observed to have calcium carbonate deposits which indicate that
some moisture has been absorbed into the concrete floor system at some time during the life of
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the facility. Random floor and roof areas were checked for structural capacity using the
following live load pressures taken from the structural plans of the building facility:
Building Area Live Load Pressure (pst)(pounds per square foot)
Roof 20
Mechanical Room Floors 125
Corridors and Assembly Areas 100
Office Areas 50
Records Storage 150
Detention Cells 40
Laundry 200
The building structure was designed in accordance with the 1982 Standard Building Code. A
copy of the 1982 Standard Building Code could not be obtained for this evaluation. However,
since these design pressures also conform to the live loads required in the 1985 Standard
Building Code, the 1985 Code was used in the evaluation.
The exterior walls are formed of 20 gauge curtain walls which connect to the building
frame. The curtain walls were checked for structural strength and deflection and found to
conform to the 1985 Standard Building Code. During our examination of the exterior surfaces of
the building, we observed that the Exterior Insulation and Finish System (E.LF.S.) panels were
not fully connected to the curtain wall. The exterior panels were warped or bowed out at many
locations and could be pushed inward indicating the failure of some of the connections. This
concern is non-structural but could allow moisture to enter the wall cavity and cause corrosion of
the steel curtain wall system.
A review of the original building plans and an observation of selected structural
components was performed. The results of our analysis did not indicate any areas that were over-
stressed or that require further study at this time.
Mold Survey:
Several areas were identified in the facility where moisture has entered into the building.
This moisture is caused by roof leaks, wall separations, ground water penetration, and window
leaks. While evaluating the building structure, the site was observed to have very little slope
away from the building structure. Some grassed areas around the building were observed to be
ponding water or actually sloping toward the building. This condition allows surface drainage to
collect at the building foundation and increase the risk of moisture exposure to the E.I.F.S. and
curtain wall system at the ground. This moisture appears to be contributing to mold spore
growth on various building components on the exterior walls of the facility.
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Physical testing for mold was performed by Alternative Construction & Environmental
Solutions, Inc. (ACES) at the facility using three methods. The retrieval of the mold used in
these analyses included the use of tape lift for mold spores that are fixed to building
components, swab sampling of suspect surface colonies, and air tests using BioCassettes for
testing airborne fungi. Mostly random locations were selected to retrieve mold samples in the
facility. However, some specimens were retrieved in potential problem areas identified by
personnel working in the facility. The locations of the test sites are indicated on the area plans
included with this report as Appendix A. The report prepared by ACES is included with this
report as Appendix B and summarized as follows:
Tape Lift and Swab Test Results:
One (1) swab specimen and twelve (12) tape lift specimens and were retrieved from
various locations in the two administrative buildings and detention tower of the facility. The
locations were selected randomly and are indicated on the area plans in Appendix A. The tape
lift specimens were retrieved and examined under a microscope in the laboratory. The tape lifts
indicated that four (4) different types of mold are fixed to building components. The mold types
identified from the tape lifts are as follows:
Tape Lift/Swab Specimen No. Location No. Mold Type Identified
AT-l 1 None
AT-2 2 None
AT-3 3 Stachybotrys
AT-4 4 Stachybotrys
AT-S 5 Stachybotrys
AT-6 6 Penicillium! Aspergillus, Brown Hyphae,
Alternaria
AT-7 7 Stachybotrys
AT-8 8 Stachybotrys
AT-9 9 None
AS-l (Swab) 10 None
T6E 11 None
TSE 12 None
T4E 13 Brown Hyphae
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Airborne Testing Results:
Nineteen (19) air quality tests were taken using BioCassettes. Two tests were taken
outside of the buildings and 17 were taken at various locations inside the facility. The exterior
air samples were taken to be used as a comparison of the mold spores detected on the inside of
the building. It is important to note that the outside air mold spore counts can differ on a daily
basis based on atmospheric and environmental conditions. However, the inside and outside air
samples were taken on the same day which should yield results that are relative. In general, the
mold counts on the inside of the building should be 30 to 80 percent of the mold counts in the
outside air.
The air sampling locations were selected randomly and are indicated on the Sampling
Location Plans in Appendix A. Some samples were taken near HV AC supply vents to evaluate
the HV AC supply air. The specimens were retrieved and sent to Environmental Microbiology
Laboratory, Inc. in San Bruno, California for examination. The results were returned indicating
that nineteen (19) different types of airborne mold are located at the facility site. Ten (10) types
of airborne mold are located outside of the facility and seventeen (17) types are located on the
inside of the facility. The mold types identified from the BioCassettes are as follows:
Test Location (Ref. Appendix A)
Mold Identification
1 2 3 4 5 6 7 8 9 10
Trichoderma X
Penicillium X X X X X X X X X
Non-Sporulating Fungi X X X X X X X X X X
Nigrospora X
Fusarium X
Engyodontium X
Cladosporium X X X X X X X X X X
Aspergillus Ochraceus X X
Aspergillus Niger X X
Aspergillus Fumigatus X X X
Alternaria X X
Aspergillus Versicolor X X X
Curvularia X X
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Memnoniella X
Stachybotrys Chartarum X X
Aphanocladium
Bipolaris/Drechslera
Blakeslea
Arthrospore
Mold Identification
11 12 13 14 15 16 17 18 19
Trichoderma
Penicillium X X X X X X X
Non-Sporulating Fungi X X X X X X X X
Nigrospora X
Fusarium X X X
Engyodontium
Cladosporium X X X X X X X X
Aspergillus Ochraceus
AspergiHus Niger X
Aspergillus Fumigatus X X
Alternaria
Aspergillus Versicolor X
Curvularia X X X
Memnoniella
Stachybotrys Charta rum
Aphanocladium X
Bipolaris/Drechslera X
Blakeslea X
Arthrospore X X
Test Location (Ref. Appendix A)
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CONCLUSIONS
Structural Evaluation:
Based on the review of the structural building plans and selected structural analyses
performed on some of the building components, it is our opinion that the building structure is
safe and conforms to the 1985 Standard Building Code. The Exterior Insulation and Finish
System or E.I.F.S. has separated at various locations allowing moisture to enter the wall cavity
and cause corrosion of the metal curtain wall studs. This building component is not a primary
structural system and should not be considered as a public safety issue. However, failure of this
system will allow moisture to enter the building and cause other non-structural problems and
should be corrected.
Mold Evaluation:
Increased moisture in the building caused by groundwater penetration, roof and window
leaks, and separations in the E.I.F.S. are believed to have caused mold to grow and become
airborne on the inside of the building. Twenty (20) different types of mold spores have been
identified at this site by using tape lifts, swabs, and air tests. Seventeen (17) types of mold spores
are located in the facility and are approximately equal to or exceed the mold spore count of the
outside air. According to the report prepared by ACES, the mold spore count that was identified
on the inside of the building should be between 30 to 80 percent of the mold spore count on the
outside of the building. Additionally, the study identified other mold spores that were not
present on the outside of the building. This finding appears to indicate that the mold is
considered to be excessive on the inside of the building and could possibly cause elevated
respiratory health risk for certain personnel working in the building that are sensitive to mold.
The tape lifts taken at the HV AC supply vents yielded negative results for mold. This finding is
believed to indicate that the existing HV AC system is not a contributing factor to the mold
problem in the buildings. Currently, there are no known national standards or maximum spore
counts that could be compared to this facility.
Six (6) air samples and 3 tape lift specimens were taken from the detention tower. Mold
was identified in the detention tower on all four levels by the BioCassette air sampling. The tape
lifts did not indicate the presence of any mold spores. However, the spore counts are much
lower inside the detention tower than in the outside air. It is therefore concluded that mold
detected on the inside of the detention tower is normal and not considered to be a problem at this
time.
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RECOMMENDED CORRECTIVE ACTION
This report has presented the results of a limited structural study of the Augusta Joint Law
Enforcement Center building structures and has also identified and evaluated several types of
mold that are present in the building. At this time, there are no recommendations for primary
structural rehabilitation. Mold spore counts appear to be elevated in the two administrative
buildings and the following corrections are recommended:
1. It is very important that the source of the moisture be removed. This will involve
regrading the site at some locations, adding additional surface drainage around the
building, correcting the failing E.I.F.S., replacing corroded metal curtain wall studs,
repairing window leaks, and repairing roof leaks.
2. After the source of the moisture has been removed, the mold in the building should be
professionally removed using proper cleaning techniques. This work should be
performed by qualified personnel that specialize in mold removal. Brushing the mold
from building surfaces is not recommended as this method could allow fixed mold to
become airborne.
3. Gypsum wall board and ceiling tiles damaged by moisture should be replaced.
4. Following the execution and completion of this corrective action work, the random
interior building areas and outside air should be retested. The air samples should
indicate that the mold spore counts on the interior of the building have dropped to less
than 80 percent of the mold spore counts on the exterior of the building.
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Appendix A
Sampling Location Plans
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Appendix B
Limited Indoor Air Quality Investigation
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ALTERNATIVE CONSTR'4CTION 6-
tNVIRc9NlvIENTALSOLUTIONS, INC.
'\
1450 Greene Street - Suite 510 · Augusta, GA 30901
Telephone: 706-262-2000 · Facsimile: 706-262-3299 · www.aces~u~a.com
September 9,2004
Client:
Cranston, Robertson, & Whitehurst
452 Ellis Street
Augusta; Georgia 30901
ATIN: Mr. Jim Cranford'
Project:
Limited Indoor Air Quality Investigation
Richmond County Judicial Center
401 Walton Way
Augusta, Georgia
Report Number: 186-103-002
1.0 SCOPE
At the request of the client, representatives of Alternative Construction & Environmental
Solutions, Inc., conducted a Limited Indoor Air Quality survey of the RJchmond County
Judicial Center at401 Walton Way, Augusta, Georgia. This survey was for the purpose
of evaluating the facilities air quality due to moisture problems.
2.0 SITE OBSERVATIONS
A walkthrough of the facility was conducted on August 10, 2004 with representatives
from the Judicial Center. During this walkthrough, numerous areas inside walls, on the
walls under the paint, and on HV AC vents were identified that had discoloration
associated with mold growth. A high level of moisture was also noted throughout the
facility. Through discussions with the representatives it was agreed that at least 10
surface and 10 culturable air samples were needed to start accessing the types and levels
of fungi located in the facility. Sampling was conducted August 23, .2004. Additional
areas were identified at this time in which sampling would help evaluate the overall air
quality. This sampling was accomplished August 24, 2004. The samples were properly
packaged and transported to Environmental Microbiology Laboratory Inc. for analysis.
Alternative Construction & Environmental Solutions, Inc.
Report Number: 186-1 03-002
Page I of4
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3.0 FINDINGS
a. Evidence of elevated levels of moisture was found throughout the facility.
Ceiling tiles showed stains from moisture, moisture damage was found in walls,
and evidence of potential fungi growth was found in walls, on ceiling tiles, and
ventilation returns. This moisture is beneficial to the growth of fungi in the
facility.
b. Sampling was conducted throughout the facility to determine the culturable air
fungi levels. This sampling, shows the airborne types and levels of fungi in
colony forming units. It is important to remember that there are no set legal
standards for the levels that can be found of fungi. Attachment I identifies the
sample number and location. Attachment II lists the fungi found, by sample
number, in colony forming units. A sample was collected outside of the facility
as welL By sampling outside of the facility. we call determine fungi that are
naturally occurring in the general area and establish a background level for it.
Attachment III and IV are charts that show the highest levels found inside the
facility compared to the levels found outside for each fungi identified as airborne.
Some types of fungi found inside the facility were not found outside.
c. There were tape and swab samples collected directly off surfaces such as walls
and ventilation returns to determine levels, if any, of fungi growing on these
objects. This helps identify fungi that is or can be airborne if the right conditions
exist. The tape and swab samples showed alternaria, aspergillus, chaetomium,
penicillium, and stachybotrys spores were detected. These fungi as well as
additional types were found in the air sampling.
4.0 Conclusions
a. Any areas where water infiltration or leaking is occurring should be repaired and
dried as soon as possible. This will help remove the moisture that the fungi need
to grow.
b. Again it is important to remember that there are no set legal standards for the
levels that can be found for these fungi. The fungi are naturally occurring and in
the air around us at all times. However, elevated levels due to added moisture in
an area can have adverse health effects. Levels that may not affect some
individuals may be more detrimental to others who are more sensitive to them.
c. As a general guideline indoor spore levels usually average 30 to 80% of the
outdoor spore levels at the time of sampling, with the same general distribution of
spore types. A substantial increase of one or two spore types which are not
reflective of the outside distribution of spore types is usually indicative of indoor
mold growth. Based on observations and sampling results there are elevated
levels of some fungi and additional types of fungi found throughout this facility.
Alternative Construction & Environmental Solutions, Inc.
Report Number; 186-103-002
Page 2 of 4
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d. Although certain items can be cleaned of visible growth, not all surfaces can be
cleaned. Items such as drop ceiling tiles, drywall, bulletin boards, etc cannot be
thoroughly cleaned due to the porous nature of the material. These items should
be 'replaced whenever feasible. Whenever replacement is not feasible cleaning
can be attempted but will be limited in its effectiveness. We can advise on the
proper ways to clean if needed.
e. It should be noted that microbiological growth can and probably will reoccur if
the source of the moisture is not corrected and maintained as appropriate. Many
of the spores are naturally occurring and willre-grow with proper moisture,
temperature and food source.
If you have any questions or need additional information, please feel free to give us a
call.
AL~nvE CONS"rRUCIION Er W\IrR.ON~;AL SOLUIIONS. INC.
1drb~
Mark E. Hartz
Vice President
MEH/CEHIlfm
Attachments
Attachment I: Sample Identification
Attachment II: Air Sample Results
Attachment III: Outside/Inside Comparison
Attachment IV: OutsidelInside Comparison
Attachment V: Laboratory Results
Alternative Construction & Environmental Solutions, Inc.
Report Number: 186-103-002
Page 3 of 4
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Attachment I
Sample Identification
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Sample Identification
DATE TYPE SAMPLE # LOCATION
23 Aug 04 Air A-I Basement, Photo Lab, on top of cabinet
23 Aug 04 Air A-2 Basement, Crime Lab, next to "Air Clean 600"
23 Aug 04 Air A-3 15t Floor, Room A 141, @ door to inner office
23 Aug 04 Air A-4 15t Floor Lobby, Room AlO1, @Water fountain
23 Aug 04 Air A-5 2nd Floor, Room A246, Judge Hamrick's Office
23 Aug 04 Air A-6 2nd Floor, Clerk of Court, Ms Newman's desk
23 Aug 04 Air A-7 2"0 Floor, Ms Mary Ann Gibb's Office
23 Aug 04 Air A-8 2no Floor, Room B203, Lt Young's Office
23 Aug 04. Air A-9 2"0 Floor, Co!. Powell's Office
23 Aug 04 Air A-I0 2nd Floor, Room B275, Sheriff's Admin Area
23 Aug 04 Tape AT-l Basement, Crime Lab Ceiling Air Vent
23 Aug 04 Tape AT-2 15t Floor, Room A 141 Window Ledge
23 Aug 04 Tape AT-3 1 st Floor, Back Comer, Window Ledge, Judge's
Office
23 Aug 04 Tape AT-4 2"0 Floor, Room A246, Judge Hamrick's Office
23 Aug 04 Tape AT-5 2"0 Floor, Clerk of Court, Window Ledge
23 Aug 04 Tape AT-6 2"0 Floor, Ms Mary Ann Gibb's Office, Ceiling
Vent
23 Aug 04 Tape AT-7 2"0 Floor, Room B203, Lt Young's Office, Wall
23 Aug 04 Tape AT-8 2"0 Floor, Room B284, J. Broome's Office, Ceiling
Vent
23 Aug 04 Tape AT-9 2"0 Floor, Room B275, Sheriff's Admin Area Vent
23 Aug 04 Swab AS-l 2"0 Floor, Ms Mary Ann Gibb's Office, Ceiling
Vent
24 Aug 04 Air JA3E 3m Floor, East Side, Tower
24 Aug 04 Air JA4W 4tn Floor, West Side, Tower
24 Aug 04 Air JA5E 51n Floor, East Side, Tower
24 Aug 04 Air JA60 61n Floor, Center, Jailer's Office
24 Aug 04 Air JA2C 2"0 Floor CID In the "Corridor"
,
24 Aug 04 Air JA2L 2"0 Floor, Lobby
24 Aug 04 Air JAIW Ground Level, Outside, On Sidewalk
24 Aug 04 Air JA20 Ground Level, Outside West Side Air Screen
24 Aug 04 Air JA6E 61n Floor, East Side, Tower
24 Aug 04 Tape T6E 6tn Floor, East Side, Plumber's Chase
24 Aug 04 Tape T5E Sin Floor, East Side, Plumber's Chase
24 Aug 04 Tape T4W 4th Floor, West Side, Plumber's Chase
Alternative Construction & Environmental Solutions, Inc.
Report Number: 186-103-002
Page 4 of4
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Attachment II
Air Sample Results
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Attachment III
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Attachment IV
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Attachment V
Laboratory Results
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Environmental
Microbiology.
Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852
5473 Kearny Villa Road, Suite 130, San Diego, CA 92123
(858) 569-5800 Fax (858) 569-5806
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www.emlab.com
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Report for:
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Mr. Cliff Hampton
Alternative Construction and Environmental Solutions
1450 Greene St.
Suite 510
Augusta, GA 30901 USA
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Regarding:
Project: RCSD/RCLED
EML 10: 112590
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APProvedbY~ ~
Janet Gallup
Senior Aerobiologist
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J/~/U
Dr. David A. Bell
Laboratory President
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This coversheet Is included with your report In order to comply with AIHA and ISO accreditation requirements,
For clarity, we report the number of significant digits as calculated: but, due to the nature of this type of biological data, the number of significant
digits that is used for interpretation should generally be one or two. All samples were received in acceptable condition unless noted in the Report
Comments portion in the body of the report, Due to the nature of the analyses performed, field blank corrections of results is not a standard
practice, .
Environmental Microbiology Laboratory, Inc, ("the Company") shall have no liability to the client or the client's customer with respect to decisions or
recommendations made, actions taken or courses of conduct Implemented by either the client or the client's customer as a result of or based upon
the Test Results. In no event shall the Company be liable to the client with respect to the Test Results except for the Company's own willful
misconduct or gross negligence nor shall the Company be liable for incidental or consequential damages or lost profits or revenues to the fullest
extent such liability may be disclaimed by law, even if the Company has been advised of the possibility of such damages, lost profits or lost
revenues. In no event shall the Company's liability with respect to the Test Results exceed the amount paid to the Company by the client therefor.
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Document Number. 200091 - Revision Number: 3
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Client: Alternative Construction and
Environmental Solutions
CIO: Mr. Cliff Hampton
Re: RCSD/RCLED
CULTURABLEAIRFUNGIREPORT
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-23-2004
Date of Receipt: 08-24-2004
Date of Report: 08-31-2004
Location: A-I: A-2: A-3: A-4:
Bio-cassette Bio-cassette Bio-cassette Bio-cassette
Comments (see below) None None None None
Lab ID-Versiont: 477721-1 477722-1 477723-1 477724-1
raw ct. cfu"'/m3 raw ct. cfu"'/m3 raw ct. cfu"'/m3 raw ct. cfu"'/m3
Acremonium
Alternaria
Aspergillus flavus
Asnemillus fumigatus 1 11 1 11
Asnergillus nidulans
Asnergillus niger 2 22
Aspergillus ochraceus 1 11
Aspemillus versicolor
Aureobasidium
Basidiomvcetes
Binolaris/Drechslera groun
Botrvtis
Chaetomium
Cladosporium 4 44 6 67 3 33 4 44
Curvularia
Engvodontium 14 156
Enicoccum
Fusarium 1 11
Memnoniella
NigrosDora I 11
Non-sporulating fungi 3 33 1 11 2 22 4 44
Paecilomvces
Penicillium 2 22 3 33 7 78 9 100
Phoma
Rhizopus
Stachvbotrvs chartarum (atra)
Trichoderma 1 11
Ulocladium
Yeasts
Positive Hole 342 342 342 342
Sample volume (liters) 90.0 90.0 90.0 90.0
TOTAL CFU* 1M3 99 289 166 221
'" cfu = colony forming units Positive hole correction chart used for all calculations AIHA EMPA T NO.: 102856
Comments:
Note: Interpretation is left to the company and/or persons who conducted the field work. Variation is an inherent part of biological sampling.
The presence or absence of a few genera in small numbers should not be considered abnormal.
NORMAL SPORE LEVELS: Indoor spore levels usually average 30 to 80% of the outdoor spore level at the time of sampling, with the same
general distribution of spore types, Filtered air, air-conditioned air, or air remote from outside sources may average 5 to 15% of the outside air
at the time of sampling. (These percentages are guidelines, only. A major factor is the accessibility of outdoor air. A residence with open doors
and windows and heavy foot traffic may average 95% of the outdoor level while high rise office buildings with little air exchange may average
2%. Dusty interiors may exceed 100% of the outdoors to some degree, but will still mirror the outdoor distribution of spore types.)
PROBLEM INTERIORS: A substantial increase of one or two spore types which are inconsistent with and non-reflective of the outside
distribution of spore types is usually indicative of an indoor reservoir of mold growth,
t A "Version" greater than 1 indicates amended data. EML ID: 112590, Page 1 on
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Client: Alternative Construction and
Environmental Solutions
C/o: Mr. Cliff Hampton
Re: RCSD/RCLED
CULTURABLEAIRFUNGlREPORT
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-23-2004
Date of Receipt: 08-24-2004
Date of Report: 08-31-2004
Location: A-5: A-6: A-7: A-8:
Bio-cassette Bio-cassette Bio-cassette Bio-cassette
Comments (see below) None None None None
Lab ID-Versiont: 477725-1 477726-1 477727-1 477728-1
raw ct. cfu*/m3 raw ct. cfu*/m3 raw ct. cfu*/m3 raw ct. cfu*/m3
Acremonium
Alternaria 1 11 1 11
Aspergillus flavus
Aspergillus fumigatus 1 11
Aspergillus nidulans
Aspergillus nil!er
Aspergillus ochraceus
Aspergillus versicolor 6 67 7 78
Aureobasidium
Basidiomvcetes
Bipolaris/Drechslera grOUP
Botrvtis
Chaetomium
Cladosporium 5 56 2 22 3 33 7 78
Curvularia 2 22' 2 22
Engyodontium
Epicoccum
Fusarium
Memnoniella 3 33
NigrosDora
Non-sporulating fungi 3 33 1 11 1 11 3 33
Paecilomvces
Penicilliwn 6 67 2 22 3 33
Phoma
Rhizopus
Stachvbotrvs chartarum (atra) 3 33 2 22
Trichoderma
Ulocladium
Yeasts
Positive Hole 342 342 342 342
Sample volume (liters) 90.0 90.0 90.0 90.0
TOTAL CFU*/M3 256 99 77 277
* cfu = colony forming units Positive hole correction chart used for all calculations AIHA EMPA T NO.: 102856
Comments:
Note: Interpretation is left to the company and/or persons who conducted the field work, Variation is an inherent part of biological sampling,
The presence or absence of a few genera in small numbers should not be considered abnormal.
NORMAL SPORE LEVELS: Indoor spore levels usually average 30 to 80% of the outdoor spore level at the time of sampling, with the same
general distribution of spore types. Filtered air, air-conditioned air, or air remote from outside sources may average 5 to 15% of the outside air
at the time of sampling. (These percentages are guidelines, only. A major factor is the accessibility of outdoor air. A residence with open doors
and windows and heavy foot traffic may average 95% of the outdoor level while high rise office buildin~s with little air exchange may average
2%. Dusty interiors may exceed 100% ofthe outdoors to some degree, but will still mirror the outdoor dIstribution of spore types,)
PROBLEM INTERIORS: A substantial increase of one or two spore types which are inconsistent with and non-reflective of the outside
distribution of spore types is usually indicative of an indoor reservoir of mold growth.
t A "Version" greater than 1 indicates amended data. EML ID: 112590, Page 2 of3
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Client: Alternative Construction and
Environmental Solutions
C/O: Mr. Cliff Hampton
Re: RCSD/RCLED
CUL TURABLE AIR FUNGI REPORT
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-23-2004
Date of Receipt: 08-24-2004
Date of Report: 08-31-2004
Location: A-9: A-lO:
Bio-cassette Bio-cassette
Comments (see below) None None
Lab ID-Versiont: 477729-1 477730-1
raw ct. cfu*/m3 raw ct. cfu*/m3
Acremonium
Alternaria
Asoefl!illus flavus
Asoergillus fumigatus
Asoergillus nidulans
Aspergillus niger 1 11
Asoergillus ochraceus 1 11
Asoergillus versicolor 1 11
Aureobasidium
Basidiomvcetes
BipolarislDrechslera grOUO
Botrvtis
Chaetomium
Cladosoorium 1 II 4 44
Curvularia
Engvodontium
Eoicoccum
Fusarium
Memnoniella
Nigrosoora
Non-soorulating fungi 4 44 4 44
Paecilomvces
Penicillium 1 11 I 11
Phoma
Rhizopus
Stachvbotrvs chartarum (atra)
Trichoderma
Ulocladium
Yeasts
Positive Hole 342 342
Sample volume (liters) 90.0 90.0
TOTAL CFU*/M3 77 121
* cfu = colony forming units Positive hole correction chart used for all calculations AIHA EMPA T NO.: 102856
Comments:
Note: Interpretation is left to the company and/or persons who conducted the field work. Variation is an inherent part of biological sampling,
The presence or absence of a few genera in small numbers should not be considered abnormal.
NORMAL SPORE LEVELS: Indoor spore levels usually average 30 to 80% of the outdoor spore level at the time of sampling, with the same
general distribution of spore types. Filtered air, air-conditioned air, or air remote from outside sources may average 5 to 15% of the outside air
at the time of sampling. (These percentages are guidelines, only. A major factor is the accessibility of outdoor air. A residence with open doors
and windows and heavy foot traffic may average 95% of the outdoor level while high rise office buildings with little air exchange may average
2%. Dusty interiors may exceed 100% of the outdoors to some degree, but will still mirror the outdoor distribution of spore types.)
PROBLEM INTERIORS: A substantial increase of one or two spore types which are inconsistent with and non-reflective of the outside
distribution of spore types is usually indicative of an indoor reservoir of mold growth.
t A "Version" greater than 1 indicates amended data. EML ID: 112590, Page 3 on
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Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-23-2004
Date of Receipt: 08-24-2004
Date of Report: 08-26-2004
Client: Alternative Construction and
Environmental Solutions
C/O: Mr. Cliff Hampton
Re: RCSD/RCLED
DIRECT MICROSCOPIC EXAMINATION REPORT
(Wet Mount)
Background Miscellaneous MOLD GROWTH: Molds seen Other General
Debris and/or Spores Present* with underlying mycelial and/or Commentstt Impression
Description sporulating structurest
Lab ID-Versiont: 477700-1: Tape sample AT-I: Tape lift
Very heavy Variety None None Normal trapping
Lab ID-Version: 477701-1: Tape sample AT-2: Tape lift
Very heavy Few None None Normal trapping
Lab ill-Version: 477702-1: Tape sample AT -3: Tape lift
Heavy Few 1 + Stachybotrys species None Mold growth
Lab ill-Version: 477703-1: Tape sample AT-4: Tape lift
Heavy Few 4+ Stachybotrys species None Mold growth
Lab ill-Version: 477704-1: Tape sample AT-5: Tape lift
Heavy Few 3+ Stachybotrys species None Mold growth
Lab ill-Version: 477705-1: Tape sample AT-6: Tape lift
Very heavy Few 2+ colorless spores typical of A few Mold growth
Penicillium / Aspergillus Stachybotrys
2+ brown hyphae with no associated spores detected.
spores, ID unknown
1 + Alternaria species
Lab ill-Version: 477706-1: Tape sample AT-7: Tape lift
Heavy Few 4+ Stachybotrys species None Mold growth
Lab ill-Version: 477707-1: Tape sample AT-8: Tape lift
Moderate Few 2+ Stachybotrys species A few Mold growth
Chaetomium
spores detected.
Lab ill-Version: 477708-1: Tape sample AT-9: Tape lift
Light Few None A few Mold growth in
Stachybotrys vicinity?
soores detected.
EML ill: 112590, Page 1 of2
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Background Miscellaneous MOLD GROWTH: Molds seen Other General
Debris and/or Spores Present'" with underlying mycelial and/or Commentstt Impression
Description sporulating structurest
Lab ID-Versiont: 477709-1: Swab sample AS-I: Swab
Moderate Few None A few Mold growth in
Stachybotrys vicinity?
spores detected.
· Indicative of normal conditions, i.e. seen on surfaces everywhere. Includes basidiospores (mushroom spores), myxomycetes, plant pathogens
such as ascospores, rusts and smuts, and a mix of saprophytic genera with no particular spore type predominating, Distribution of spore types
seen mirrors that usually seen outdoors,
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t Quantities of molds seen growing are listed in the MOLD GROWTH column and are graded 1+ to 4+, with 4+ denoting the highest numbers.
tt Some comments may refer to the following: Most surfaces collect a mix of spores which are normally present in the outdoor environment.
At times it is possible to note a skewing of the distribution of spore types, and also to note "marker" genera which may indicate indoor mold
growth. Marker genera are those spore types which are present normally in very small numbers, but which multiply indoors when conditions
are favorable for growth.
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:t: A "Version" greater than 1 indicates amended data.
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EML ill: 112590, Page 2 of2
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Client: Alternative Construction and
Environmental Solutions
C/O: Mr. Cliff Hampton
Re: RCSD/RCLED
CULTURABLE AIR FUNGI REPORT
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-24-2004
Date of Receipt: 08-26-2004
Date of Report: 08-31-2004
Location: JA6E JA5E JA3E JAlW
Comments (see below) None None None None
Lab ID-Versiont: 478602-1 478603-1 478604-1 478605-1
raw ct. cfu*/m3 raw ct. cfu*/m3 raw ct. cfu*/m3 raw ct. cfu*/m3
Acremonium
Alternaria
Aohanoc1adium 1 II
Arthrosoore- former
AsnefQillus flavus
Asnerl!illus fumigatus 1 11
Asnerl!illus nidulans
Asoemillus niger 2 22
Asoemillus ochraceus
AsnefQillus versicolor 1 11
Aureobasidium
Basidiomvcetes
Binolaris/Drechslera grOUO 1 11
Blakeslea 1 11
Botrvtis
Chaetomium
Cladosnorium 11 122 22 256 7 78 92 1.190
Curvularia 3 33
Eoicoccum
Fusarium 1 11 4 44
NiQTosnora 1 11
Non-snorulatinl! fungi 1 11 4 44 6 67
Paecilomvces
Penicillium 3 33 7 78
Phoma
Rhizonus
Stachvbotrvs chartarum (atra)
Uloc1adium
Yeasts
Positive Hole 342 342 342 342
Sample volume (liters) 90.0 90.0 90.0 90.0
TOTAL CFU*/M3 166 300 189 1.400
* cfu = colony forming units
Comments:
Positive hole correction chart used for all calculations
AIHA EMPATNO.: 102856
Note: Interpretation is left to the company and/or persons who conducted the field work. Variation is an inherent part of biological sampling,
The presence or absence of a few genera in small numbers should not be considered abnormal.
NORMAL SPORE LEVELS: Indoor spore levels usually average 30 to 80% of the outdoor spore level at the time of sampling, with the same
general distribution of spore types. Filtered air, air-conditioned air, or air remote from outside sources may average 5 to 15% of the outside air
at the time of sampling. (These percentages are guidelines, only. A major factor is the accessibility of outdoor air. A residence with open doors
and windows and heavy foot traffic may average 95% of the outdoor level while high rise office buildin~s with little air exchange may average
2%. Dusty interiors may exceed 100% of the outdoors to some degree, but will still mirror the outdoor distribution of spore types.)
PROBLEM INTERIORS: A substantial increase of one or two spore types which are inconsistent with and non-reflective of the outside
distribution of spore types is usually indicative of an indoor reservoir of mold growth.
t A "Version" greater than 1 indicates amended data. EML ID: 112782, Page lof3
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Client: Alternative Construction and
Environmental Solutions
CIO: Mr. Cliff Hampton
Re: RCSDIRCLED
CULTURABLEAIRFUNGlREPORT
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-24-2004
Date of Receipt: 08-26-2004
Date of Report: 08-31-2004
Location: JA4W JA2C JA2L JA6JO
Comments (see below) None None None None
Lab ill-Version!: 478606-1 478607-1 478608-] 478609-1
raw ct. cfu*/m3 raw ct. cfu*/m3 raw ct. cfu*/m3 raw ct. cfu*/m3
Acremonium
Alternaria
Aohanoc1adium
Arthrosoore- former 1 11
Asoenzillus flavus
Asoergillus fumigatus I 11
Asoergillus nidulans
Aspergillus niger
Aspergillus ochraceus
Aspergillus versicolor
Aureobasidium
Basidiomvcetes
Bioolaris/Drechslera grOUO
Blakeslea
Botrvtis
Chaetomium
Cladosoorium 25 289 11 122 9 100
Curvularia 1 11 I 11
Epicoccum
Fusarium 1 11
Nigrospora
Non-sporulating fungi 3 33 4 44 6 67 3 33
Paecilomvces
Penicillium 5 56 1 11 3 33 2 22
Phoma
Rhizopus
Stachvbotrvs chartarum (atra)
Uloc1adium
Yeasts
Positive Hole 342 342 342 342
Sample volume (liters) 90.0 90.0 90.0 90.0
TOTAL CFU*1M3 400 77 222 166
* cfu = colony forming units
Comments:
AIHA EMPATNO.: ]02856
Positive hole correction chart used for all calculations
Note: Interpretation is left to the company and/or persons who conducted the field work. Variation is an inherent part of biological sampling.
The presence or absence of a few genera in small numbers should not be considered abnormal.
NORMAL SPORE LEVELS: Indoor spore levels usually average 30 to 80% of the outdoor spore level at the time of sampling, with the same
genera] distribution of spore types. Filtered air, air-conditioned air, or air remote from outside sources may average 5 to 15% of the outside air
at the time of sampling. (These percentages are guidelines, only. A major factor is the accessibility of outdoor air, A residence with open doors
and windows and heavy foot traffic may average 95% of the outdoor level while high rise office buildin~s with little air exchange may average
2%. Dusty interiors may exceed 100% of the outdoors to some degree, but will still mirror the outdoor distribution of spore types.)
PROBLEM INTERIORS: A substantial increase of one or two spore types which are inconsistent with and non-reflective of the outside
distribution of spore types is usually indicative of an indoor reservoir of mold growth,
t A "Version" greater than 1 indicates amended data. EML ill: 112782, Page 2 of 3
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Client: Alternative Construction and
Environmental Solutions
c/o: Mr. Cliff Hampton
Re: RCSDfRCLED
CULTURABLEAIRFUNGIREPORT
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www.emlab.com
Date of Sampling: 08-24-2004
Date of Receipt: 08-26-2004
Date of Report: 08-31-2004
Location: JA20: JA20:
Blank Blank
Comments (see below) None None
Lab ID-Versiont: 478610-1 478611-1
raw ct. cfu*/m3 raw ct. cfu*/m3
Acremonium
Alternaria
Aohanoc1adium
Arthrosoore- former 1 N/A
Asnerl!illus flavus
Asnemillus fumigatus
Asoemillus nidulans
Asoemillus ni2:er
Asoenrillus ochraceus
Asoergillus versicolor
Aureobasidium
Basidiomvcetes
BioolarisfDrechslera grOUO
Blakeslea
Botrvtis
Chaetomium
Cladosnorium 22 N/A
Curvularia
Eoicoccum
Fusarium
Ni2:I'osoora
Non-soorulatin2: fun2:i 3 N/A
Paecilomvces
Penicillium 5 N/A
Phoma
Rhizoous
Stachvbotrvs chartarum (atra)
Ulocladium
Yeasts I N/A
Positive Hole 342 0
Samole volume (liters) 0.0 0.0
TOTAL CFU*/M3 0 N/A
* cfu = colony forming units Positive hole correction chart used for all calculations AIHA EMP A T NO.: 102856
Comments:
Note: Interpretation is left to the company and/or persons who conducted the field work. Variation is an inherent part of biological sampling.
The presence or absence of a few genera in small numbers should not be considered abnonnal.
NORMAL SPORE LEVELS: Indoor spore levels usually average 30 to 80% of the outdoor spore level at the time of sampling, with the same
general distribution of spore types, Filtered air, air-conditioned air, or air remote from outside sources may average 5 to 15% of the outside air
at the time of sampling, (These percentages are guidelines, only. A major factor is the accessibility of outdoor air. A residence with open doors
and windows and heavy foot traffic may average 95% of the outdoor level while high rise office buildings with little air exchange may average
2%, Dusty interiors may exceed 100% of the outdoors to some degree, but will still mirror the outdoor distribution of spore types,)
PROBLEM INTERIORS: A substantial increase of one or two spore types which are inconsistent with and non-reflective of the outside
distribution of spore types is usually indicative of an indoor reservoir of mold growth.
t A "Version" greater than 1 indicates amended data, EML 10: 112782, Page 3 of3
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Client: Alternative Construction and
Environmental Solutions
C/O: Mr. Cliff Hampton
Re: RCSDIRCLED
DIRECT MICROSCOPIC EXAMINATION REPORT
(Wet Mount)
Environmental Microbiology Laboratory, Inc.
1150 Bayhill Drive, Suite 100, San Bruno, CA 94066
(650) 829-5800 Fax (650) 829-5852 www,emlab.com
Date of Sampling: 08-24-2004
Date of Receipt: 08-26-2004
Date of Report: 08-27-2004
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Background Miscellaneous MOLD GROWTH: Molds seen Other General
Debris and/or Spores Present* with underlying mycelial and/or Commentstt Impression
Description sporulating structurest
Lab lD-Versiont: 478612-1: Tape sample T4W
Very heavy Very few None None Normal trapping
Lab lD-Version: 478613-1: Tape sample T5E
Very heavy Very few None None Normal trapping
Lab lD-Version: 478614-1: Tape sample T6E
Very heavy Few < 1+ brown hyphae with no None Minimal mold
associated spores, ID unknown growth
· Indicative of normal conditions, i.e, seen on surfaces everywhere, Includes basidiospores (mushroom spores), myxomycetes, plant pathogens
such as ascospores, rusts and smuts, and a mix of saprophytic genera with no particular spore type predominating, Distribution of spore types
seen mirrors that usually seen outdoors,
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t Quantities of molds seen growing are listed in the MOLD GROWTH column and are graded 1+ to 4+, with 4+ denoting the highest numbers.
tt Some comments may refer to the following: Most surfaces collect a mix of spores which are normally present in the outdoor environment.
At times it is possible to note a skewing of the distribution of spore types, and also to note "marker" genera which may indicate indoor mold
growth, Marker genera are those spore types which are present normally in very small numbers, but which multiply indoors when conditions
are favorable for growth,
I
t A "Version" greater than I indicates amended data,
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EML ill: 112782, Page) of I
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Cranston, Robertson & Whitehurst, P.C.
ENGINEERS - PLANNERS . SURVEYORS
452 Ellis Street. P.O. Box 2546
Augusta, Georgia 30903
www.crwpc.com