HomeMy WebLinkAboutNC0083887_Renewal Application_31 December 2014
Julie A. Grzyb, Environmental Engineer
NC DENR - Division of Water Resources
WQ Permitting Section - NPDES
512 N. Salisbury Street
91h Floor — Archdale Building
Raleigh, NC 27604
Ms. Grzyb:
RECEIVED/DENR/DWR
JAN - 2 2015
Water Quality
Permitting Section
Enclosed you will find the renewal application (Short Form C in Appendix A) and other
supporting documents for Charlotte Douglas International Airport's NPDES Individual Permit
renewal request. The permit primarily allows discharge of stormwater, treated wastewater, spent
de-icing fluid, and washwater. Other permitted non-stormwater discharges may include
uncontaminated groundwater, foundation drains, air-conditioning condensate, springs, waterline
and hydrant flush, water from footing drains, and flows from riparian habitats and wetlands.
Several airport tenants should be listed as co-permittes on the new permit. The co-permittee
request list is included as Table 1 (Appendix D). All co-permittees will be bound to the terms
and conditions of the new permit and will also be required to attend annual Stormwater Pollution
Prevention Training given in the fall of each year. The current permit expires June 30, 2015.
Outfall Monitoring
Since re -issuance of the current permit in 2011, the airport has monitored 27 basin outfalls, each
stormwater basin and outfall is summarized in Table 3. Figure 1 (Appendix F) displays a
topographic map identifying each outfall. Figure 2 displays drainage area locations and the
outfalls they discharge to. Periodic analytical testing is performed at seven outfalls (001, 002,
003, 004, F, H, and K), 004 is an in stream monitoring point, see Tables 4, 4A, 413, 4C, 4D, 4E,
4F, and 4G for analytical summaries. The remaining twenty basins are assessed visually at least
two times per year, as summarize by Table 5. It is important to note that the North Carolina Air
National Guard (NCANG) maintains a separate NPDES permit for their operations on Airport
property between Runway 36R/18L and Airport Drive. The NCANG reportedly monitors five
outfalls adjacent to that roadway, three of which are also monitored (visually) by the Airport.
Table 3 denotes the three outfalls which are monitored by both NCANG and the Airport.
The airport and its contractor are currently working to finalize the new 2014 Stormwater
Pollution Prevention Plan (SPPP). Once the SPPP is complete, the updated detailed site plan
will be submitted (early 2015) as part of an amendment to this application.
Nt-w nivrfane
No new outfalls have been in use since the 2010 application. New outfall location(s) may be
appropriate and expected, given the anticipated March 2015 completion of the Airport's "Rental
Car Village" located north of the Airfield off Wilkinson Boulevard, see Figure 3 for location.
URS Corporation
6000 Fairview Road, Suite 200
Charlotte, NC 28210
Tel: 704.522.0330
Fax: 704.522.0063
www.urscorp.com
RECEIVEDIDENRIDWR
JAN - 2 2015
Airport De -Icing Water Quality
Permitting Section
A single contractor (IDS, LLC) performs aircraft de-icing for all regularly scheduled commercial
flights at CLT. Aircraft are sprayed on de-icing pads located adjacent to runway 5/23, or, on the
south cargo ramp. General Aviation de-icing services are provided by Wilson Air Center,
located on Airport drive and to the east of runway 36R/18L. Figure 3 displays the de-icing
locations described above. Aircraft de-icing is performed primarily in the Coffee Basin, Ramp
Basin, and the FBO Basin. No significant changes are planned with respect to where de-icing
will occur in the future.
In accordance with permit special condition A9 (h), the Airport has been submitting de-icing
usage data on an annual basis. The information has been submitted in the Month of June with
the May Discharge Monitoring Report (DMR). Tables 2, 2A, and 2B summarize de-icing fluid
usage during 2011-2014.
Best Management Practices (BMPs)
Best Management Practices are summarized by Appendix E. Certification of the Airport's
SPPP is included in Appendix G.
Facility Changes
Although operations at the airport have not significantly changed during the permit period,
significant facility improvements and infrastructural changes have occurred. Item No. 7 in
Appendix B further lists significant changes that have occurred at the facility.
Supplemental information required for renewal of individual NPDES Stormwater Permit is
verified in Appendix C. Should you or other members of your review team need additional
information, please do not hesitate to contact me at (704) 716-0734.
Sincerely,
URS Corporation — North Carolina
P�1-11
James P. McDorman, P.G.
Senior Geologist
Cc: Mr. Jimmy Jordan, P G , Charlotte Aviation Department
Appendix A
Short Form C — NPDES Permit Application
RECEIVEDIDENRIDWR
JAN - 2,:2015
Water Quality
Permitting Section
NPDES PERMIT APPLICATION - SHORT FORM C - Minor Industrial
Minor industrial, manufacturing and commercial facilities.
Mail the complete application to:
N. C. Department of Environment and Natural Resources
Division of Water Quality / NPDES Unit
1617 Mail Service Center, Raleigh, NC 27699-1617
NPDES Permit Number INCO083887
Please print or type.
1. Contact Information:
Owner Name
Facility Name
Mailing Address
City
State / Zip Code
Telephone Number
Fax Number
e-mail Address
City of Charlotte
Charlotte Douglas International Airport
P.O. Box 19066
Charlotte
North Carolina 28219
(704) 359-4000
(704) 359-4950
jdjordan@charlotteairport.com
2. Location of facility producing discharge:
Check here if same as above
Street Address or State Road
City
State / Zip Code
County
5501 Josh Birmingham Parkway
Charlotte
North Carolina 28208
Mecklenburg
3. Operator Information:
Name of the firm, consultant or other entity that operates the facility. (Note that this is not referring to the
Operator in Responsible Charge or ORC)
Name City of Charlotte - Aviation
Mailing Address 5601 Wilkinson Boulevard
City Charlotte
State / Zip Code North Carolina 28208
Telephone Number (704) 359-4916
Fax Number (704) 359-4950
4. Ownership Status:
Federal ❑ State ❑ Private ❑ Public
Page 1 of 4 C-MI 10/08
NPDES PERMIT APPLICATION - SHORT FORM C - Minor Industrial
Minor industrial, manufacturing and commercial facilities.
11. Frequency of discharge: Continuous ® Intermittent ❑
If intermittent: Days per week discharge occurs: Duration:
12. Types of wastewater discharged to surface waters only
Discharge
Flow
GALLONS PER DAY
Sanitary - monthly average
None known RECEIVEDIDENRIDWR
Utility water, etc. - monthly average
None'Known JAN - 2::2015
Process water - monthly average
None known Water Qua{
Stormwater - monthly average
Approximately 100 million gallons
Other - monthly average
Included above
Explain: Holding water-ASIG fuel farm
Monthly Average
total discharge (all types)
Approximately 100 million gallons
13. Number of separate discharge points: See Table 3. Outfall Identification number(s) See
Table 3.
14. Name of receiving stream(s) (Provide a map shouting the exact location of each outfall, including
latitude and longitudes '
Stormwater Outfall Information is summarized by Table 3 and is also illustrated by Figure 1.
15. Effluent Data [for new or proposed discharges] - Please refer to Tables 4 (A,B,C,D,E,F, and G)
and 5.
Provide data for the parameters listed. Temperature and pH shall be grab samples, for all other parameters 24-hour
composite sampling shall be used. If more than one analysis is reported, report daily maximum and monthly average.
If only one analysis is reported, report as daily maximum.
NOTE: Permittees requesting renewal should complete the table ONLY for the parameters
currently monitored. Summarize the past 3 years of effluent data.
Parameter
Daily
Maximum
Monthly
Average
Units of
Measurement
Biochemical Oxygen Demand (BOD5)
Chemical Oxygen Demand (COD)
Total Organic Carbon
Total Suspended Solids
Ammonia as N
Temperature (Summer)
Temperature (Winter)
pH
Fecal Coliform (If sanitary waste is
present)
Total Residual Chlorine (if chlorine is
used)
Page 3 of 4 C-MI 10108
NPDES PERMIT APPLICATION - SHORT FORM C - Minor Industrial
Minor industrial, manufacturing and commercial facilities.
16. List all permits, construction approvals and/or applications (check all that apply and provide permit
numbers or check none if not applicable):
Type Permit Number Type Permit Number
Hazardous Waste (RCRA)
UIC (SDWA)
NPDES
PSD (CAA)
Non -attainment program (CAA)
NCD986216281 NESHAPS (CAA)
Ocean Dumping (MPRSA)
NCO083887 Dredge or fill (Section 404 or CWA)
Other
17. List any chemicals that may be discharged (Please list and explain source and potential
amounts.)
Benzene, toluene, ethyl benzene, xylenes (outfall 001 only, ppb concentrations)
Oil and grease (45 mg/L maximum)
Biodegradeable detergents from vehicle, equipment, and aircraft washing
Propylene glycol from winter de-icing operations
MBAS (detergent/deodorizers)
Ammonia - Urea used as pavement de-icer in winter months
18. Is this facility located on Indian country? (check one)
Yes ❑ No
19. Applicant Certification
I certify that I am familiar with the information contained in the application and that to the
best of my knowledge and belief such information is true, complete, and accurate.
Printed name of Pei on Signing
of
Date
North Carolina General Statute 143-215.6 (b)(2) provides that: Any person who knowingly makes any false
statement representation, or certification in any application, record, report, plan, or other document files or
required to be maintained under Article 21 or regulations of the Environmental Management Commission
implementing that Article, or who falsifies, tampers with, or knowingly renders inaccurate any recording or
monitoring device or method required to be operated or maintained under Article 21 or regulations of the
Environmental Management Commission implementing that Article, shall be guilty of a misdemeanor punishable
by a fine not to exceed $25,000, or by imprisonment not to exceed six months, or by both. (18 U.S.C. Section
1001 provides a punishment by a fine of not more than $25,000 or imprisonment not more than 5 years, or both,
for a similar offense.)
Page 4 of 4 C-MI 10/08
Appendix B
Response to NCDENR Questions/hAormation Requests
In addition to the Short Form C renewal application, following are some questions that must be
answered in order to process the CDIA permit renewal. On page 3 a questionnaire titled
"SUPPLEMENTAL INFORMATION REQUIRED FOR RENEWAL OF INDIVIDUAL NPDES
STORMWATER PERMIT" is attached. Some of the information requested on that form is
contained in the 12 questions below but please review them and add any additional information
requested to your answers if not already addressed.
1. Are there Co-Permittees to be listed on the NPDES permit? Yes, see Table 1.
2. Does the facility have over 1,000 annual jet departures? Yes
3. Does the facility use 460,000 gallons or more of normalized ADF per year? No, see
Tables 2, 2A, and 2B.
4. In accordance with 40 CFR parts 9 and 449 — There shall be no discharge of airfield
pavement deicers containing urea. To comply with this limitation, any existing point
source must certify annually that it does not use airfield deicing products that contain
urea or alternatively, airfield pavement discharges at every discharge point must
achieve the numeric limitations for ammonia as nitrogen in Table 1, prior to any
dilution or commingling with any nonde-icing discharge.
TABLE 1—BAT LIMITATIONS
Wastestream Pollutant Daily maximum
Airrield Pavement Deicing .........................................Ammonia as Nitrogen ............................................... 14.7
If the Airport is going to continue the use of urea based products a sampling station
must be developed and identified at every stormwater discharge point that can possibly
contain pavement de-icers. This information should be addressed and included on the
Table/Chart created to answer question # 6 below. In stream sampling is conducted
for each de-icing event at 002 and 004. Analytical sampling for ADF is conducted
at 002, 003, 004, F, H, and K for each de-icing event. See Tables 411, 4C, 4D, 4E,
4F, and 4G.
5. Total Glycol and Urea usage during 2011 - 2014. Report usage data broken down by
year and month for Propylene Gylcol (type I, type II, etc.), Ethylene Glycol, Total
Glycol (gallons), and Urea (gallons). No need to report months when no glycol or
ureas are used. See Tables 2, 2A, and 2B.
6. Provide a topographic map identifying each outfall and another map(s) showing each
drainage area and the outfall(s) it will discharge to. Provide a table or chart which lists
each outfall, its location (description, latitude and longitude), a description of treatment
provided prior to discharge, receiving stream, and activities performed in that drainage
area (Jet fuel storage (amount), De-icing, vehicle washing, anti -icing, etc.). Questions
11, 12, and 17 in the Short Form C application should be answered for each outfall and
answers can be put into a simple chart or table if preferred. See Figures 1 and 2; also
see Table 3 in Appendix D.
7. Summarize the changes that have occurred since the last permit application was
submitted. Clearly identify new outfalls and drainage areas in maps and tables
requested above.
Page 1 of 3
Changes that have occurred since last application was submitted include the
following, also see Table 3:
• Construction of Rental Car Village (Perimeter Area of Airport),
• Construction of Valet Parking Deck 1 (CLT Center),
• Construction of Valet Parking Deck 2 (CLT Center),
• Construction of Taxiway D North Extension,
• Construction of Taxiway D South Extension,
• Construction of Airport Entrance Road,
• Danga Lake Dam,
• K West Detainment Structure,
• Airport Consolidate De-icing Facility,
• Airport De-icing Pads,
• Norfolk Southern Intermodal Facility, and
• Hourly Parking Deck
8. Summarize last 10-12 data points for each sampled parameter from outfalls 001
through 004. Provide the mean and max. Parameters detected below detection levels
should be listed as less than the detection level used (i.e. < 1 ug/L). For outfalls 001,
002, 003, answer question 15. Data collected during the last three years may be used to
answer the question. If samples were not taken for any of the parameters listed a
sample should be taken and tested. See Tables 4, 4A, 4B, 4C, 4D, 4E, 4F, and 4G.
9. Ammonia as nitrogen data collected during the last three years for any of - the
s"tormwater outfalls should be summarized in a table. See Tables 413, 4C, 4D, 4E, 4F,
and 4G.
10. If possible, new outfalls (being requested in this permit application but already in use)
which drain areas exposed to ADF, fuels or surfaces where industrial activities are
occurring should be tested at least one time as specified under the requirements listed
for outfall 001 Part II, Section E. (1.) in the current permit and the data submitted with
the permit application. An acute toxicity test is not necessary but grab samples should
be collected and analyzed for COD and Ammonia as N for the new outfalls in use as
well. No new outfalls are already in use.
11. See Stormwater questionnaire below. See Appendix C.
12. Summarize Acute Toxicity (%) tests from the current permit effective date to present -
date for outfalls 001, 002, and 003. See Tables 4A, 4B, 4C, 4D, 4E, 4F, and 4G.
Please simply refer to these tables or charts requested above in the Short Form C where
appropriate, no need to duplicate answers.
These questions apply to all Stormwater Outfalls excluding Outfall 001 (Jet Fuels. Tank Farm)
Page 2 of 3
Appendix C
Supplemental Information Required for Renewal of
Individual NPDES Stormwater Permit
SUPPLEMENTAL INFORMATION REQUIRED FOR RENEWAL OF INDIVIDUAL
NPDES STORMWATER PERMIT
Two copies of each of the following shall accompany this submittal in order for the application
to be considered complete:
Initials
1
(Do not submit the site Stormwater Pollution Prevention Plan)
A current Site Map from the Stormwater Pollution Prevention Plan. The location of
industrial activities (including storage of materials, disposal areas, process areas and
loading and unloading areas), drainage structures, drainage areas for each outfall,
building locations and impervious surfaces should be clearly noted.
A summary of Analytical Monitoring results during the term of the existing permit
(if your permit required analytical sampling). Do not submit individual lab reports.
The summary can consist of a table including such items as outfall number,
parameters sampled, lab results, date sampled, and storm event data. *
A summary of the Visual Monitoring results. Do not submit individual monitoring
reports. The summary can consist of a table including such items as outfall number,
parameters surveyed, observations, and date monitoring conducted.
A summary of the Best Management Practices utilized at the permitted facility.
Summary should consist of a short narrative description of each BMP's in place at
the facility. If the implementation of any BMP's is planned, please include
information on these BMP's.
5. A short narrative describing any significant changes in industrial activities at the
permitted facility. Significant changes could include the addition or deletion of
work processes, changes in material handling practices, changes in material storage
practices, and/or changes in the raw materials used by the facility.
6. Certification of the development and implementation of a Stormwater Pollution
Prevention Plan for the permitted facility (Sign and return attached form).
If the final year analytical monitoring of the existing permit term has not been completed prior to
filing the renewal submittal, then the last years monitoring results should be submitted within 30
days of receipt of the laboratory reports. (i.e. do not withhold renewal submittal waiting on lab
results)
Representative storm sampling may now be conducted anytime during the year (the April to
November window has been eliminated) and the representative rainfall event is now defined as a
storm event that measures greater than 0.1 inches and is preceded by at least 72 hours in which
no storm event measuring greater than 0.1 inches has occurred.
Page 3 of 3
Appendix D
Tables
1. Airport's Co-Permittee Request List
2. Summary of De -Icing Usage 2011-2014
3. Summary of Stormwater Basins and Stormwater Outfalls
4. Summary of Laboratory Analytical Reports — Outfalls 001, 002, 003, 004,
F, H, and K
S. Summary of 2011-2014 Qualitative Monitoring Reports
CDIA TENANT LIST REVISED 12/22/2014
Table 1
��.� #� ;.�h� Co�Periiiltteesfor�NP,DESnPerm_it+NC_ 0083887=r•. "g` 3r'�'>`
Advantage Rent a Car
Air Service International Group (ASIG)
Air General
Air Canada
American Airlines
American Eagle
Avis Budget Group
Bank of America
Carolinas Historic Aviation Commission and Museum
Carolina Aircraft Services
Charlotte -Douglas International Airport - CLT Center
Charlotte -Mecklenburg Police Department (CMPD) Aviation
Charlotte Fire Department Station ARFF 41
Charlotte Fire Department Station No. 17
Coca-Cola Aviation
Delta Air Lines
Delta Global Services
Dollar Thrifty Automotive Group, Inc.
Duke Energy
Enterprise (Enterprise Holdings, Inc)
Express Jet
Family Dollar
Federal Express
Frontier Airlines
GAT (Ground Aviation Terminal)
G2 Secure Services
Hertz Car Rental
Insell Air
International De-icing Services LLC, (IDS)
HMS Host
JetBlue Airways
JetStream Ground Services, Inc.
LSG Sky Chefs
Lufthansa German Airlines
MedCenter Air
National/Alamo Car Rental
Piedmont Airlines GSE
Piedmont Catering
PSA Airlines
Roush Air
Sonic Aviation
Southwest Airlines
Page 1 of 2
CDIA TENANT LIST REVISED 12/22/2014
�''���� �,�Co Perinittees�for`•iNPDES+PerinitNC00838.87�``, ��-���< �
SPX Hangar
Teal Aviation
United Airlines
United Parcel Service
US Airways
US Airways Base Maintenance Facility
US Airways Cargo
US Airways Catering
US Airways Engine Shop
US Airways Express
US Airways GSE Maintenance Facility
US Airways Line Maintenance Facility
US Airways Stock Distribution Center
Wilson Air Center
Worldwide Flight Services
Worldwide Flight Services GSE
�•�''`,R:�• �'++'.�:�. ,q.._y'. s'�:Lwsy. s� ^'#["'•`;go-:;; �"": %�', ..'yh, '`•y'�."f •t
#�,,£ ..7�:3 ": a�ae a,,'��.:'��,.a�.�-; �.ea • urs: " ;x: -� r.'� �tr.�� �Y,',_ xf�-.. i ��'�,2`-.. �`o� n. - �:;?�:'���r��:'F.,.:�sr»� f
Page 2 of 2
Table 2-Summary of Aircraft De -Icing Fluid Usage - Charlotte Douglas International Airport, Winter Season of October 2011- April 2012
*Usage In Gallons of Fluid Prior to Dilution
US Airways �xpress�
General Aviation
rvwnuny ivLaia w 44/ lbl9 1703 2849 85 5
Pl - Propylene Glycol, Type 1
P4- Propylene Glycol, Type 4
El - Ethylene Glycol, Type 1
E4 - Ethylene Glycol, Type 4
* Tenants not seen on this list used 0 gallons of de-icing fluid in the 2011- 2012 winter season.
Totals
366
324
2053
60
209
0
1171
0
1082
1479
Total Gallons Used: 6744
Table 2A-Summary of Aircraft De -Icing Fluid Usage - Charlotte Douglas International Airport, Winter Season of October 2012 - April 2013
*Usage In Gallons of Fluid Prior to Dilution
•
�•
,
Fluid Type
US Airways Exp-ress
-'
Lufthansa German,
munimy i otais 4 ilo
P1 - Propylene Glycol, Type 1
P4- Propylene Glycol, Type 4
E1 - Ethylene Glycol, Type 1
E4 - Ethylene Glycol, Type 4
* Tenants not seen on this list used 0 gallons of de-icing fluid in the 2012 - 2013 winter season.
4j1
Z0789
33110
7846
Total Gallons Used:
0
Totals
522
1069
32780
0
294
0
24223
0
2306
903
62896
Table 26-Summary of Aircraft De -Icing Fluid Usage - Charlotte Douglas International Airport, Winter Season of October 2013 - April 2014
*Usage In Gallons of Fluid Prior to Dilution
Month
Oct-13
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
Fluid Type
P1
P4
E1
E4
PI
P4
E1
E4
P1
P4
E1
E4
P1
P4
E1
E4
P1
P4
E1
E4
P1
P4
E1
E4
P1
P4
E1
E4
Airtran /Southwest
American
US Airways
FEDEX
JetBlue*
Insel Air*
US Airways Express
UPS
United
Delta
Lufthansa German
General Aviation
131
191
272
679
49
1251
354
75
26
60
136
351
270
125
80
37
0
116
439
399
6771
3508
39125
19137
1400
2078
0
0
0
280
150
895
1900
125
680
250
0
0
0
0
0
0
0
0
0
0
0
0
0
0
13
138
100
51
0
3643
2115
7552
3873
1157
1283
0
0
0
16
276
180
76
186
95
91
0
336
443
925
200
543
620
140
99
184
288
817
292
1352
574
232
0
0
0
0
240
174
85
0
354
75
0
11
85
172
16
1185
338
139
1 55
�j
Monthly Totals 385
1459
1970 21453 78317
8575
0
P1 - Propylene Glycol, Type 1
P4- Propylene Glycol, Type 4
E1 - Ethylene Glycol, Type 1
E4 - Ethylene Glycol, Type 4
* These airlines did not require de-icing during the winter season, due to their operational schedules out of CLT
Totals
3002
1085
72973
4280
0
0
19925
920
3207
2001
Total Gallons Used: 112159
Table 3 - Summary of Stormwater Basins and Stor mwater Outfalls - Charlotte Douglas International Airport NCO083887
Basin Name
General Description
Outfall Location
Coordinates
Treatment
Recelving Water
Activities
Tlcer Creek •
Alrm}t Fu015torage Farm
North of Fuel Farm -Outfa11001
35-13'45 99" North
OWS, Holding Pond
Tlcer Branch
Vehicle Fueling Area. Maln Aircraft Fuel Storage Area
2 8 acres, 96%Impervious
8D'56'55 10' West
antl 3 GAC Canisters
Coffey/ Ram
Dreln's majority of airfield
NC 160 and Coffee Creek - Outfa11002
35011150A1' North
Coffey Creek
aircraft and vehicle fueling, maintenance, sanitation
1824 Acres, 30%Impervious
80'56'53.52' West
services, deicing, washln& urge handling, painting
striping, chemical storage and use, pesticide & herbicide usage
FBO'
Corporate Aviation Area
West of Airport Drive near Sentry post
35"12'2464"North
Holding Pond
Taggart Creek
aircraft and vehiclefuelln& maintenance, sanitation
East of Runway 36R/38L
Outfa11003
80'55'44 67" West
services, deicing, washing, cargo handling, painting
Instream Station'
Background monitoring point
Between Josh Birmingham and
35.13'S6"North
Nane-Instrcam samplln point
Wilkinson BNd, behind CLT center
80'S6'19' West
strl In , chemical storage and use, pesticide & herbicide usage
ANG"
Alr National Guard Facilities
East of Minuteman Way
35'13'12.00' North
Taggart Creek
Under pirreft by NCANG
BD'S5'3639' West
T-hangar "
414 acres, 85% Impervious
35'12'45 57` North
Aircraft and vehicle fueling and maintenance, de4cing, sanitary Service, washing,
chemical storage, pesticide & herbicide use, flrellghting drill discharges
BD'55'40 55' West
R-23
Carolina's Aviation Museum
Northeast of Runway 23
35'13'28 29' North
Holding Pond
Taggart Creek
Chemical and fuel usage and storage, aircraft maintenance
66 At.,, 21%Imp— us
acress Airport Drive
a7'55'4875"West
pesticide herbicide usage. equipment washing
Taggart Creek ••
Northeast Area
east of Minuteman Way
35'12'59 05' North
19%lmpeiv].a
just SW of Winston Container
8(r55'3164' West
None
Taggart Creek
Aircraft fueling, chemical Stange, equipment storage
Coke, Wachovla, Duke Energy, NCANG not Included
Air Cargo
South Portion Runway 36R
Same as F80
35'12'24 64' North
Holding Pond
Taggart Creek
almnifl and vehicle fueling, maintenance, sanitation
Yorkmort Cargo Area
90'55'4467"West
services, deicing, washing, cargo handling, aintln
striping, chemical storage and use, pesticide & herbicide usage
Sentry Post
14%Impervious
35'12'11.54' North
SD'S5'3710' West
Runway 36R
southeast Airport Area
East of Yor1mr-1 Road
35'12'03 64" North
None
Taggart Creek
chemical storage, equipment malntenance, washing
80055'40 68' West
esticide and herbldtle usage, painting, stripping, Vehicle
A Basin
North of T..lway N
North of Old Dowd toad
35-13'49- North
none
Titer Branch
No activities
80'57'54' West
B Basin
North/East of Runway 18N
Between RR and Old Dowd Rd
35-1349' North
none
Tlcer Branch
No activities
80'5r54• West
C Basin
Northeast comer Runway 1811
Northeast edge of pmpe
309343'Noh
n
Noactvtes
85'
12West
D Basin
Northeast comer Runway 18R
Northeast edge of rePerry
135-13'3r North
none
Lake W lie
Aircraft Movement Area / Periodic generator fueling
80'58'13" West
E Basin
Northeast corner Runway ISR
Northeast edge of pro erty
35'13'32'North
Lake Wylie
No actwltles
80'58'12" West
-
F Basln'
North runway area
between 1.485 and Wallace Neel Rd
35'13'19' North
on.
Lake Wylie
Aircraft Movement Area only as of January 6, 2010
80'S811' West
G Basin
North runwaya
between 1-485 and Wallace Neel Rd
35'13'03' North
Paw Creek
Aircraft Movement Area onlyas of January6, 2010
go. 8.07' West
Danga Lake
Dana Lake
West of 1485, Dana Dam
35'1149" North
Pond
Dana Lake
No activities
'
80'5820" West
H Besln'
large area between N and 5
between 1.4&5 and Wallace Neel Rd.
35'1Y51" North
none
Dana Lake
Aircraft Movement Area only as of January 6, 2010
80'59D6' West
K West Basin-
small area .west of runway
west of future K West pond
35'3Y25' North
Pond
Little Paw Creek
No activities
18R/36L
80'SW17' West
K Basin
South Runwa 36L Area
between 1.485 and Wallace Neel Rd
35012'24' North
none
Little Paw Creek
Aircraft Movement Area only as of January 6, 2010
BXS8'04" West
L Basin
South Runway 36L Area
between 1485 and Wallace Neel Rd
3512'08" North
none
Beaverdam Creek
jAircraft Movement Area / P riodicilieneratOrfuellng
80'58'05' west
_
M Basin
Southwest Airport, off 18R/36L
West of Wallace Neel Read
35'11'S0'North
none
Beaverdam Creek
No activities
80'5803' West
N Basin
Almost Identlul te Coffee
Same as Coffee / Ramp Outfall
35'11'50' North
none
Coffee Creek
Aircraft Movement Area only as of January 6, 2010
Ramp Basin listed above
80'56'53' West
O Basin
South of T,.Iw.y S, between
Southeast Runway 23/36C
35'12'03" North
none
Coffee Creek
Firefighting ddll discharges
Runways 36C and 36L
80'56'54"West
R Basin
South area
south of Runway 36C
35'11'S5" North
none
Coffee Creek
Aircraft Movement Area
80'S6'5Y West
=Outfall requires periodic 0.nalytlol
Testing
• Monitored and sampled by North Carolina Air National Guard
:names since December ZU09
CLT [enter
Charlotte Aviation Dept. Offices and
I NA
35'11'01' North
Nene
Sugar Creek
Offlce and Malnenrfoamance space, Business Valet Parking No pavement de-I<ersor ADF
Alrport Parking Deck
80'56'05"West
Watershed
used Nodebrlsedlscharge
Rental Car Village
Maintenance and upkeep of Rental
35'14'24' North
Paw Creek
Vehicle maintenance, cleaning and washing No pavement de-icers or ADF used No
I E"o Rackham Or I
Vehicles
NA."-
80'57'03"West
none
Watershed
debris or foam discharge
•=future
Table 4 - Outfall 001, Summary of Monthly Effluent Analytical Results NCO083887
Date
Flow
T5s
Oil and Grease
pH
Benzene
Ethylbenzene
Toluene
Xylene
10/25/2011
NM
< 5.0
<5.0
6.83
< 0.5
< 0.5
< 0.5
< 3.0
11/29/2011
0.08
NM
<5.0
NM
NM
NM
NM
NMI
1/27/2012
0.065
< 5.0
< 5.0
6.78
< 0.5
< 0.5
< 0.5
< 3.0
2/28/2012
0.24
< 5.0
5.1
7.13
< 0.5
< 0.5
< 0.5
< 3.0
3/31/2012
0.43
< 5.0
< 5.0
7.11
< 0.5
< 0.5
< 0.5
< 3.0
4/25/2012
0.75
< 1.0
< 5.0
6.73
< 0.5
< 0.5
< 0.5
< 3.0
5/10/2012
0.41
7.0
< 5.0
7.12
< 0.5
< 1.0
< 1.0
< 3.0
6/30/2012
0.37
13
< 5.0
6.88
< 0.5
0.72
1.7
8.7
7/25/2012
0.45
17
< 5.0
6.81
< 0.5
< 0.5
< 0.5
< 3.0
8/28/2012
0.70
< 5.0
< 5.0
6.29
< 0.5
< 0.5
< 0.5
< 3.0
9/18/2012
0.43
< 5.0
< 5.0
6.74
< 0.5
< 0.5
< 0.5
< 3.0
10/31/2012
0.45
44
< 5.0
7.01
< 0.5
< 0.5
< 0.5
< 3.0
11/28/2012
0.50
< 5.0
< 5.0
6.82
< 0.5
< 0.5
< 0.5
< 3.0
12/31/2012
0.28
< 5.0
< 5.0
6.78
< 0.5
< 0.5
< 0.5
< 3.0
1/31/2013
0.14
12.00
< 5.0
7.03
2.30
6.7
15
187
3/28/2013
0.08
< 5.0
< 5.0
7.27
< 0.5
< 0.5
< 0.5
< 3.0
4/29/2013
0.08
< 5.0
< 5.0
7.27
< 0.5
< 0.5
< 0.5
< 3.0
5/19/2013
0.08
7.30
< 5.0
7.14
< 0.5
< 0.5
< 0.5
< 3.0
6/4/2013
0.08
< 5.0
< 5.0
7.01
< 0.5
< 0.5
< 0.5
< 3.0
7/30/2013
0.05
< 5.0
< 5.0
7.07
< 0.5
< 0.5
< 0.5
< 3.0
8/31/2013
0.06
5.40
< 5.0
6.83
< 0.5
< 0.5
< 0.5
< 3.0
9/23/2013
0.25
< 5.0
< 5.0
7.00
< 0.5
< 0.5
< 1.0
5.20
11/26/2013
0.20
< 5.0
< 5.0
7.11
< 0.5
< 0.5
< 1.0
< 3.0
12/17/2013
0.18
< 5.0
< 5.0
7.09
< 0.5
< 0.5
< 0.5
< 3.0
1/31/2014
0.06
< 5.0
< 5.0
7.12
NM
< 0.5
< 0.5
< 3.0
3/18/2014
0.24
< 5.0
< 5.0
7.03
N M
< 0.5
< 0.5
< 3.0
4/30/2014
0.00
< 5.0
< 5.0
7.04
< 0.5
< 0.5
< 0.5
8.90
5/31/2014
0.08
< 5.0
< 5.0
6.83
NM
< 0.5
< 0.5
< 3.0
6/17/2014
0.14
7.2
<5.0
7.19
<0.5
<0.5
<0.5
<3.0
7/31/2014
0.084
< 5.0
< 5.0
6.89
< 0.5
< 0.5
< 0.5
< 3.0
8/30/2014
0.060
62
< 5.0
6.84
< 0.5
< 0.5
0.71
< 3.0
9/25/2014
0.037
< 2.6
< 5.0
7.04
< 0.5
< 0.5
< 0.5
< 3.0
Units
million gal/day
mg/liter
mg/liter
Std. units
ug/liter
ug/liter
ug/liter
ug/liter
Daily Maximum
45
45
6-9
51
11
Notes:
NM = Not measured
Effluent samples collected after the oil -water separator/retention pond treatment system
Table 4A - Outfall 001, Summary of Quarterly Effluent Analytical
Results NCO083887
Date
Total Nitrogen
Total Phosphorus
Acute Toxicity
January-12
1.1
0.09
Pass
April-12
1.2
< 0.5
Pass
July-12
1.0
0.1
Pass
October-12
1.0
0.14
Pass
January-13
2.5
<0.05
Pass
April-13
0.62
0.18
Pass
September-13
0.94
0.07
Pass
December-13
<0.70
< 0.050
Pass
March-14
12
13
Pass
June-14
3.50
0.24
Pass
September-14
< 0.14
< 0.050
Fail
Units
mg/liter
mg/liter
pass/fail
Benchmark
30
2
Note:
Effluent samples collected after the oil -water separator/retention pond treatment
system
Table 413- Outfall 002, Summary of Quarterly Analytical Results NCO083887
Date
Total Rainfall
Turbidity
Acute Toxicity
COD
BOD
TPH-
Oil and Grease
TSs
Detergents
(MBAs)
Nitrogen
(NH3)
Nitrogen
(NO3+ NO2)
Total
Nitrogen
Total
Phosphorus
PH
Ethylene
Glycol
Propylene
Glycol
12/7/2011
0.5
350
NA
81
6.8
< 5.0
28
0.15
0.50
0.20
0.21
0.19
6.7
NA
NA
2/20/2012
0.3
15
Pass
< 50
< 8.0
NA
NA
NA
< 0.10
NA
NA
NA
7.03
< 271
< 245
3/31/2012
0.2
10
NA
< 5.0
4.6
< 5.0
9.8
0.16
< 0.10
0.25
< 0.11
096
6.97
NA
NA
5/8/2012
0.2
13
NA
97
31
< 5.0
< 5.0
0.77
0.26
1.3
3.0
0.27
7.02
NA
NA
8/28/2012
0.2
10
NA
< 5.0
< 5.0
< 5.0
15
0.13
< 0.10
1.3
< 0.60
< 0.05
6.98
NA
NA
12/16/2012
0.2
11.5
NA
< 5.2
< 2.0
< 5.0
< 5.0
< 0.014
028
0.32
< 0.50
< 0.05
7.04
NA
NA
2/18/2013
0.3
5
Fail
<5.0
140
NA
NA
NA
<0.10
NA
NA-
NA
6.83
<170
NM
3/12/2013
05
16
NA
< 5 0
< 3.0
< 5.0
16
0.14
< 0.10
0.42
< 0.60
< 0.056
6.88
NA
NA
6/17/2013
0.3
7.5
NA
< 5.0
< 5.0
< 5.0
< 5.0
< 0.015
0.86
< 0.10
1.1
0.064
1 7.11
NA
NA
9/22/2013
0.7
3
NA
<3.5
4
< 5.0
< 5.0
< 0.10
0.49
0.23
1.1
0.070
7.27
NA
NA
11/26/2013
3.9
< 1.0
NA
< 5.0
< 2.0
< 5.0
40
< 0.10
0.1
0.18
< 0.60
< 0.05
6.89
NA
NA
1/28/2014
0.9
10
Pass
< 50
< 2.0
NA
NA
NA
< 0.10
NA
NA
NA
6.94
<265
< 170
2/17/2014
2.2
5
Pass
< 50
< 3.0
NA
NA
NA
0.12
NA
I NA
NA
6.83
<265
< 170
3/16/2014
08
11
NA
< 50
6.4
< 5.0
< 5.0
0.11
0.23
0.18
< 0.60
< 0.050
6.91
NA
NA
6/9/2014
0.3
< 5.0
NA
< 3.5
16
< 5.0
< 5.0
0.11
0.15
0.46
1.2
0.95
6.79
NA
NA
9/24/2014
2
< 5.0
NA
< 3.5
< 2.0
< 5.0
< 1.0
< 0.015
0.14
0.3
< 0.14 1
0.11
687
NA
NA
Units
in
NTU
I PosslfoLl
mg/liter
mg/liter
m /liter
I mg/liter
I mg/liter
mg/liter
mg/liter
mg/liter I
ma/liter
std. units
m /liter
m /liter
Benchmark Values
50
1120
30
15 1
100
1 0.5
7.2
10
30 1
2
1 6-9
NA
NA
Analytical Summary of De-icing Event Instream Sampling
Date
Dissolved Oxygen
Turbidity
pH
2/20/2012
8.0
15
7.03
2/18/2013
7.8
5
7.8
1/28/2014
7.14
10
6.94
2/17/2014
7.47
5
6.83
Units
I mg/liter
I NTU
I std. units
Benchmark
Values
5
50
6-9
Table 4C - Outfall 003, Summary of Quarterly Analytical Results NCO083887
Date
Total Rainfall
Turbidity
Acute Toxicity
COD
BOD
TPH-
Oil and Grease
T55
Detergents
(MBAs)
MBAs(NH3)
Nitrogen
( a)
Nitrogen
NO
(NO3 2)
Total
Nitrogen
g
Total
Phosphorus
p
pH
Ethylene
Glycol
Y
Propylene
Glycol
Y
12/7/2011
0.50
70
NA
98
5.40
< 5.0
83
015
0.50
0.20
0.21
0.19
6.63
NA
NA
2/20/2012
0.30
11
Pass
< 50
30
NA
NA
NA
< 0.10
NA
NA
NA
7.40
< 271
20,500
3/31/2012
0.20
11
NA
< 5.0
5.40
< 5.0
1.30
0.15
< 0.10
0.18
< 0.11
010
6.93
NA
NA
5/8/2012
0.20
6.5
NA
< 5.2
9.90
< 5.0
19
0.47
0.11
1.1
1.90
0.13
6.85
NA
NA
8/29/2012
0.20
12
NA
< 5.0
< 5.0
< 5.0
< 5.0
0.14
< 10
0.32
< 0.60
< 0.05
6.45
NA
NA
12/16/2012
0.20
7
NA
< 5.0
< 5.0
< 5.0
< 5.0
0.14
0.27
0.28
0.58
< 0.05
7.00
NA
NA
2/18/2013
0.30
NA
Pass
<5.0
87
NA
NA
NA
<0.10
NA
NA
NA
6.79
<170
NM
3/12/2013
0.50
16
NA
< 5.0
< 3.0
5.30
6.60
0.13
< 0.10
0.42
< 0.60
< 0.050
6.89
NA
NA
6/17/2013
0.30
6
NA
< 5.0
< 5.0
< 5 0
< 5.0
< 0.015
0.83
< 0.10
1.90
0.069
7.04
NA
NA
9/22/2013
0.70
5
NA
<3.5
2.3
< 5.0
< 5.0
< 0.010
0.55
0.20
1.1
0.053
7.18
NA
NA
11/26/2013
3.90
< 1.0
NA
< 5.0
< 2.0
< 5.0
< 5.0
0.16
0.11
0.17
< 0.60
< 0.05
6.79
NA
NA
1/28/2014
0.90
NA
Pass
< 50
4.40
NA
NA
NA
< 0.10
NA
NA
NA
NM
<265
< 170
2/17/2014
2.20
NA
Pass
< 50
< 3.0
NA
NA
NA
0.13
NA
NA
NA
NM
<265
< 170
3/16/2014
0.80
10
NA
< 50
6.40
< 5.0
< 5.0
0.10
0.23
0.19
< 0.60
< 0.050
6.84
NA
NA
6/9/2014
0.30
< 5.0
NA
i < 3.5
7.40
< 5.0
< 5.0
0.11
0.18
0.47
1.40
0.96
7.01
NA
NA
9/24/2014
2
< 5.0
NA
< 3.5
< 2.0
< 5.0
< 1.0
< 0.015
0.11
0.28
< 0.14
0.1
6.93
NA
NA
Units
I in
NTU
I passail
mg/liter
I mg/liter
mg/liter
I mg/liter
I mg/liter
mg/liter
mg/liter
mg/liter
mg/liter
std. units
mg/liter
m /Irter
Benchmark Values
1
1 50
1
120
1 30
15
1 100
1 0.5
7.2
10
30
2
6-9
NA
NA
Table 41) - Outfall 004, Summary of Quarterly Analytical Results NCO083887
Date
Total Rainfall
Turbidity
Acute Toxicity
COD
BOD
TPH-
Oil and Grease
T55
Detergents
(MBAs)
Nitrogen
(NH3)
Nitrogen
(N%+ NOz)
Total
Nitrogen
Total
Phosphorus
pH
Ethylene
Glycol
Propylene
Glycol
12/7/2011
0.50
46
NA
< 5.2
< 4.0
< 5.0
38
0.23
< 5.0
0.22
< 0.0025
0.16
6.80
NA
NA
2/20/2012
0.30
16
Pass
< 50
< 8.0
NA
NA
NA
< 0.10
NA
NA
NA
6.79
< 271
< 245
3/31/2012
0.20
12
NA
< 5.0
5.3
< 5.0
13
1.4
< 0.10
< 0.10
0.90
0.11
6.89
NA
NA
5/8/2012
0 20
2
NA
150
23
< 5.0
21
1.3
1.0
1.0
3.1
0.16
6.97
NA
NA
8/29/2012
0.20
11
NA
< 5.0
< 5.0
< 5.0
< 5.0
0.12
< 0.22
0.34
< 0.60
1 < 0.05
6.42
NA
NA
12/16/2012
0.20
1 10
NA
< 5.0
< 2.0
< 5.0
< 5.0
< 0.14
027
0.29
0.50
< 0.05
6.62
NA
NA
2/18/2013
0.30
5
Pass
<5.2
38
NA
NA
NA
<0.10
NA
NA
NA
7.11
<170
NM
3/12/2013
0.50
14
NA
< 5.0
< 3.0
< 5.0
13
0.10
< 0.10
0.40
< 0.60
0.52
6.85
NA
NA
6/17/2013
0.30
7
NA
< 5.0
< 5.0
1.4
< 5.0
< 0.015
0.92
< 0.10
1.40
0.065
6.96
NA
NA
9/22/2013
0.70
< 1.0
NA
<3.5
2.60
1.0
< 5.0
< 0.10
048
0.22
1.00
0.055
6.99
NA
NA
11/26/2013
3.90
< 1.0
NA
< 5.0
17
< 0.1
< 5.0
0.11
< 0.01
0.18
< 0.10
< 0.05
6.88
NA
NA
1/28/2014
0.90
10
Pass
< 50
29
NA
NA
NA
3.40
NA
NA
NA
6.81
<265
< 170
2/17/2014
2.20
10
Fail
< 50
< 3.0
NA
NA
NA
< 0.10
NA
NA
NA
6.97 •
<265
< 170
3/16/2014
0.80
13
NA
< 50
6
< 5.0
< 5.0
< 0.10
0.23
0.18
< 0.60
< 0.050
7.01
NA
NA
6/9/2014
0.30
< 5.0
NA
< 3.5
2
< 5.0
< 5.0
0.10
0.17
0.47
1.40
0.95
6.84
NA
NA
9/24/2014
2
< 5.0
NA
< 3.5
< 2.0
< 5.0
< 1.0
< 0.015
0.12
0.34
0.87
< 0.05
6.84
NA
NA
Units
in
NTU
ass/fail
mg/liter
mg/liter
mg/liter
mg/liter
mg/liter I
mg/liter
I mg/liter I
mg/liter
mg/liter
std. units
mg/liter
m /liter
Benchmark Values
50
120
30
15
100
0.5 1
7.2
1 10 1
30
2
6-9
NA
NA
Analytical Summary of De-icing Event Instream Sampling
Date
Dissolved
Oxygen
Turbidity
pH
2/20/2012
7.65
16
6.79
2/18/2013
8.05
5
7.11
1/28/2014
6.87
10
6.81
2/17/2014
7.05
10
6.97
t7n-itsI
mg/liter
1-7-ul
std. units
Benchmark
Values
5
50
6-9
Table 4E - Clutfall F, Summary of Quarterly Analytical Results NCO083887
Date
Total Rainfall
Turbidity
Acute Toxicity
COD
BOD
TPN-
Oil and Grease
Tss
Detergents
MBAs
Nitrogen
NH ,)
Nitrogen
NO + N
( . �)
Total
Nitrogen
g
Total Phosphorus
pH
Ethylene
Glycol
Propylene
Glycol
12/7/2011
050
60
NA
50
460
< 5.0
12
017
1
< 0 0026
1
065
6.64
NA
NA
2/20/2012
0.30
17
Pass
<50
<80
NA
NA
NA
<0.10
NA
NA
NA
7.13
<271
<245
3/31/2012
0.20
12
NA
<5.0
6.6
<5.0
6
0.11
<0.10
0.30
0.69
0.16
712
NA
NA
6/26/2012
0.20
30
NA
<5 2
12
< 5.0
1 34
0.42
2.10
< 0.10
2.4
0.11
6.84
1 NA
NA
8/28/2012
0.20
16
NA
<5.0
<5.0
<50
<5.0
0.11
<061
<0.10
0.95
<0.69
6.48
NA
NA
12/16/2012
0.20
10
NA
<5.2
2.0
<50
19
<0.14
0.27
0.32
060
<0.05
6.75
NA
NA
2/18/2013
0.30
NA
Pass
<50
<70
NA
NA
NA
<0.10
NA
NA
NA
6.91
<170
NM
3/12/2013
0.50
10
NA
< 5.0
< 3 0
<50
5
017
< 1.0
042
< 0.60
0 054
6.89
NA
NA
6/17/2013
0.30
8
NA
<5.0
<5.0
<50
<5.0
<0015
0.84
<0.01
1.20
0.061
7.18
NA
NA
9/22/2013
0.70
< 1.0
NA
<2 3
23
< 5.0
<50
0.11
0.70
0.15
1.00
< 0.050
7.11
NA
NA
11/26/2013
3.90
8
NA
<2.0
<2.0
<50
<50
013
<0.10
0.14
<0.10
<0.05
710
NA
NA
1/28/2014
090
NA
Pass
<so
< 2 0
NA
NA
NA
<0.10
NA
NA
NA
NM
<265
<170
2/17/2014
2.20
NA
Pass
<so
<3.0
NA
NA
NA
0.12
NA
NA
NA
NM
<265
<170
3/16/2014
080
10
NA
<50
6.70
<5.0
<5.0
0.11
0.23
0.19
<0.60
<0.050
698
NA
NA
6/9/2014
0.30
<5.0
NA
<3.5
4.60
<5.0
<5.0
<0.10
0.17
0.45
1.40
098
7.11
NA
NA
9/24/2014
2
<5.0
NA
<3.5
<20
<5.0
<1.0
<0.015
0.12
0.36
<0.14
<0.05
6.94
NA
NA
Units
in
NTU
ass/ a!
mg/liter
m /titer
mg/liter
mg/liter
m /Irter
mg/liter
in liter
mg/liter
mg/liter
std units
mg/liter
mg/liter
Benchmark Values
50
120
30
15
100
0.5
7.2
SO
30
2
6.9
NA
NA
Table 4F - Outfall H, Summary of Quarterly Analytical Results NCO083887
Date
Total
Rainfall
Turbidity
Acute
Toxicity
COD
SOD
TPH
Oil and
Grease
Tss
Detergents
(MBAs)
Nitrogen
(NH3)
Nitrogen
(N%+ NO2)
Total
Nitrogen
Total Phosphorus
PH
Ethylene
Glycol
Propylene
Glycol
12/7/2011
0.50
26
NA
66
12
< 5.0
12
0.18
1.20
< 0.0026
< 0.0026
0.28
6.67
NA
NA
2/20/2012
0.30
17
Pass
< 50
< 8.0
NA
NA
NA
< 0.10
NA
NA
NA
7.18
< 271
< 245
3/31/2012
020
9
NA
< 5.0
< 4.0
< 5.0
32
0.14
0.23
0.23
< 0.11
0.12
7.08
NA
NA
6/26/2012
0.20
3
NA
< 5.2
1 12
1 < 5.0
50
0.14
1.9
< 0.10
22
0.11
6.76
NA
NA
8/28/2012
0.20
15
NA
<5.0
<5.0
<50
<5.0
0.12
<0.10
<010
<0.60
<0.071
650
NA
NA
12/16/2012
020
10
NA
< 5.2
< 2.0
< 5.0
11
< 0 14
0.28
0.30
0.56
< 0 05
679
NA
NA
2/18/2013
0.30
NA
Pass
< 5.0
< 7.0
NA
NA
NA
< 0.10
NA
NA
NA
7.04
< 170
NM
3/12/2013
0.50
12
NA
< 5 0
< 3.0
< 5.0
13.00
012
< 0.10
042
< 0.60
< 0.050
673
NA
NA
6/17/2013
0.30
8
NA
< 5.0
4.9
< 5.0
< 5 0
< 0 015
0.93
< 0.10
1.10
0.056
6.89
NA
NA
9/22/2013
070
< 1.0
NA
<3.5
2.70
< 5.0
< 5.0
< 0.10
0.55
0.20
1.10
< 0.050
708
NA
NA
11/26/2013
3.90
6
NA
< 5.0
< 2 0
< 5.0
< 5 0
0.10
< 040
0.16
< 0.10
< 0.05
704
NA
NA
1/28/2014
0.90
NA
Pass
< 50
< 2.0
NA
NA
NA
< 0.10
NA
NA
NA
NM
<265
< 170
2/17/2014
2.20
NA
Pass
< 50
< 3 0
NA
NA
NA
012
NA
NA
NA
NM
<265
< 170
3/16/2014
0.80
10
NA
< 50
6.10
< 5.0
< 5.0
0.11
0.23
0.19
< 0 60
< 0.050
7.05
NA
NA
6/9/2014
0.30
< 5.0
NA
< 3 5
4.00
< 5 0
< 5.0
< 0.10
0.15
0.40
120
1.00
7.15
NA
NA
9/24/2014
2
< 5 0
NA
< 3.5
< 2.0
< 5.0
< 1.0
< 0 O15
0 13
033
< 0.14
< 0.05
695
NA
NA
Units
in
NTU
ass/fad
mg/hter
m /liter
mg/liter
mg/liter
m /liter
mg/Irter
mg/liter
mg/liter
mg/liter
std. units
I mg/liter
mg/liter
Benchmark Values
50 1
1
120 1
30
15
100
1 0.5
1 7.2
10
30
2
6-9
1 NA
NA
Table 4G - Outfall K, Summary of Quarterly Analytical Results NCO083887
Date
Total Rainfall
Turbidity
Acute Toxicity
COD
BOD
TPH
Oil and Grease
Tss
Detergents
(MBAs)
Nitrogen
(NHj
Nitrogen
(NO3+ NO,)
Total
Nitrogen
Total Phosphorus
PH
Ethylene
Glycol
Propylene
Glycol
12/7/2011
050
71
NA
59
5.60
< 5.0
30
0.23
1.20
0 15
1.30
1.70
6.72
NA
NA
2/20/2012
030
19
Pass
< 50
< 8 0
NA
NA
NA
< 0.10
NA
NA
NA
7 23
< 271
< 245
3/31/2012
0.20
0.5
NA
310
480
< 5 0
5.2
0.12
< 0.010
0.35
1.7
0.18
7.1
NA
NA
6/26/2012
0.20
2.5
NA
<52
7.90
<5.0
25
0.16
2.3
<0.10
2.2
0.11
NA
NA
8/28/2012
0.20
10
NA
<5.0
<5.0
<5.0
<5.0
<0.10
<021
035
<060
<0.05
NA
NA
12/16/2012
020
10
NA
< 5 2
< 2.0
< 5.0
9.4
< 0.14
0.27
0.30
0.61
< 0 05
NA
NA
2/18/2013
0.30
NA
Pass
<50
<7.0
NA
NA
NA
<0.10
NA
NA
NA
N-6.93
<170
NM
3/12/2013
050
16
NA
< 5.0
< 3.0
<50
14
0.15
< 0 10
0.40
< 0.60
< 0.050
NA
NA
6/17/2013
0.30
8
NA
<50
<5.0
<5.0
<5.0
<0,015
0.84
<0.10
1.20
0.055
NA
NA
- 9/22/2013
0.70
< 1.0
NA
<3.5
2 70
< 5.0
< 5.0
1.0
0 54
0 20
0.96
0.054
NA
NA
11/26/2013
3.90
6
NA
<50
<2.0
<5.0
<50
0.14
<0.10
0.17
<010
<0.05
7.09
NA
NA
1/28/2014
0.90
NA
Pass
<50
<2.0
NA
NA
NA
<0.10
NA
NA
NA
NM
<265
<170
2/17/2014
2.20
NA
Pass
< 50
< 3 0
NA
NA
NA
012
NA
NA
NA
NM
<265
< 170
3/16/2014
08
10
NA
< 50
5.50
< 5,0
< 5.0
0.11
023
0 18
< 0.60
< 0 050
7.01
NA
NA
6/9/2014
03
< 5 0
NA
< 3 5
7.00
< 5.0
< 5.0
< 0.10
0 16
045
1.30
0.98
7.07
NA
NA
9/24/2014
2
< 5,0
NA
< 3 5
< 2.0
< 5.0
< 1 0
< 0.015
0.13
0.33
< 0 14
< 0.05
6.94
NA
NA
Units
in
NTU
pass/all
mg/liter
mg/liter
mg/liter
mg/liter
mg/liter
m /liter
mg/liter
mg/liter
mg/liter
std units
mg/liter
mg/liter
Benchmark Values
50
120
30
15
100
0.5
7.2
10
30
2
6-9
NA
NA
Table 5 - Summary of Qualitative Monitoring Reports NCO083987
N.—ber-December 2012
Outfall ID
Date
Structure
Color
Odor
•Carhy ll-
S
••Floating Solids
1-5
•••Suspended Solids ll
51
Feem
Oil Sheen
Eroskm or
Deposition
Titer Creek
11/04/2011
Stream
Clear
None
1
1
1
No
No
No
002
12/17/2012
Stream
Clear
None
1
1
1
No
No
No
Coffee Creek
11/04/2011
Stream
Clear
None
1
1
1
No
No
No
003
12/17/2011
Ditch
Clear
None
1
1
1
No
No
No
FBO
11/29/2011
Mich
Clear
None
1
1
1
No
No
No
OD4
12/17/2011
Stream
Clear
None
1
1
1
No
No
No
B
11/29/2011
Basin
Clear
None
1
1
1
No
No
No
D
12/17/2011
Ditch
Clear
None
1
1
1
No
No
No
F
12/17/2011
Basin
Clear
None
1
1
1
No
No
No
G
11/29/2011
Basin
Clear
None
1
1
1
No
No
No
K
12/17/2011
Basin
Clear
None
1
1
1
No
No
No
L
11/29/2011
Basin
Clear
None
1
1
1
No
No
No
M
12/17/2021
Basin
Clear
None
1
1
1
No
No
No
R
12/17/2012
Basin
Clear
None
I
1
1
No
No
No
RW23
12/17/2011
Basin
Clear
None
1
1
1
No
No
No
Air Cargo
12/17/2011
Basin
Clear
None
1
1
1
No
No
No
Danga Lake
11/04/2011
Basin
Clear
None
1
1
1
No
No
No
Sentry Post
12/17/2011
Basin
Clear
None
1
1
1
No
No
No
R-36
11/04/2011
Basin
Clear
None
1
1
1
No
No
No
Notes:
• where 1Is clear, 5Is very cloudy
••where 1 Is no solids, 5 Is covered with floating solids
• 'where 1 Indicates no wilds, 51s extremely muddy
lanuarv-March 2011
Outfall ID
Data
Structure
Color
Odor
Clarity ll-
5
••Floating Sol ids
1-5
•••Suspended Solids (1
5)
Foam
Oil Sheen
Erosion or
Deposition
Ticer Creek
02/17/2012
Stream
Clear
None
1
1
1
No
No
No
002
01/27/2012
Stream
Clear
None
1
1
1
No
No
No
Coffee Creek
02/17/2012
Stream
Clear
None
1
1
1
No
No
No
003
01/18/2012
Ditch
Clear
None
1
1
1
No
No
No
004
01/18/2012
Stream
Clear
None
1
1
1
No
No
No
FRO
02/17/2012
Ditch
Clear
None
1
1
1
No
No
No
B
03/18/2012
Basin
Clear
None
1
1
1
No
No
No
D
01/27/2012
Ditch
Clear
None
1
1
1
No
No
No
F
02/DS/2012
Basin
Clear
None
1
1
1
No
No
No
G
03/18/2012
Basin
Clear
None
1
1
1
No
No
No
K
0210512012
Basin
Clear
None
1
1
1
No
No
No
L
03/18/2012
Basin
Clear
None
1
1
1
No
No
No
M
02/05/2012
Basin
Clear
None
1
1
1
No
No
No
R
03/18/2012
Basin
Clear
None
1
1
1
No
No
No
RW23
01/12/2012
Basin
Clear
None
1
1
1
No
No
No
Air Cargo
D'
Basin
'In
Clear
None
1
1
1
No
No
No
Danga Lake
03/24/2012
Basin
Clear
None
1
1
1
No
No
No
Sentry Post
01/12/2012
Basin
Clear
None
1
1
1
No
No
No
R-36
03/24/2012
Basin
Clear I
None
1 1
1
1
No
No
No
• where 1 Is clear, S Is very cloudy
`•where 1 Is no wilds, 5 is covered with floating solids
` 'where 1 Indicates no solids, 51s extremely muddy
Aadl-lun. 20t2
Outfall ID
Data
Structure
Color
Odor
•Clarity ll-
••Floating Solldf
•••Suspended Solids l3{
5
Faam
OII Shaan
Erosion or
Deposl Ion
Ticer Creek
04/19/2012
Stream
I Clear
None
1 1
1
1
No
No
No
002
05/23/2012
Stream
Clear
None
1
1
1
No
No
No
Coffee Creek
D4/19/2012
Stream
Clear
None
1
1
1
No
No
No
003
06/12/2012
Ditch
Clear
None
1
1
1
No
No
No
004
06/12/2012
Stream
Clear
None
1
1
1
No
No
No
FBO
04/19/2012
Ditch
Clear
None
1
1
1
No
No
No
B
04/19/2012
Basin
Clear
None
1
1
1
No
No
No
0
05/23/2012
Ditch
Clear
None
1
1
1
No
No
No
F
05/23/2012
Basin
Clear
None
1
1
1
No
No
No
G
04/19/2012
Basin
Clear
None
1
1
1
No
No
No
K
05/23/2012
Basm
Clear
None
1
1
1
No
No
No
L
04/19/2012
Basin
Clear
None
1
1
1
No
No
No
M
05/23/2012
Basin
Clear
None
1
1
1
No
No
No
R
OS/23/2012
Basin
Clear
None
1
1
1
No
No
No
RW23
06/12/2022
Basin
Clear
None
1
1
1
No
No
No
Air Cargo
06/12/2012
Basin
Clear
None
1
1
1
No
No
No
Danga Lake
04/19/2012
Basin
Clear
None
1
1
1
No
No
No
Sentry Post
06/12/2012
Basin
Clear
None
1
1
1
No
No
No
• where I is clear, 51s very cloudy
-where 1 Is no solids, 51s covered with floating soles
• •where 1Indicates no solids, S Is extremely muddy
lulv-Seotemb-2012
Outh111D
Data
Structure
Color
Odor
•Chrky(I-
5
••Floating Solids
1.5
•••5uspended Sollds(l
5
Foam
0115hpn
Erosion or
De klon
Tice, Creek
07/02/2012
Stream
Clear
None
1
I
1
No
No
No
Coffee Creek
07/02/2012
Stream
Clear
None
1
1
1
No
No
No
003
08/18/2012
Ditch
Clear
None
1
1
I
No
No
No
004
09/18/2012
Stream
Clear
None
1
1
3
No
No
No
FBO
07/02/2012
Ditch
Clear
None
1
1
1
No
No
No
B
07/24/2012
Basin
Clear
None
1
1
1
No
No
No
D
08/18/2012
Ditch
Clear
None
1
1
1
No
No
No
F
08/19/2012
Basin
Clear
None
3
11
1
No
No
No
G
07/02/2012
Basin
I Clear
None
I 1
1
1
No
I No
No
K
09/18/2012
Basin
Clear
None
1
1
1
No
No
No
L
07/02/2012
Basin
Clear
None
1
1
1
No
No
No
M
09/19/2012
Basin
Clear
None
I
1
1
No
No
No
R
07/02/2012
Basin
Clear
None
1
1
1
No
No
No
RW23
09/02/2012
Basin
Clear
None
1
1
1
No
No
No
Air Cargo
09/02/2012
Basin
Clear
None
1
1
1
No
No
No
Dana Lake
07/02/2012
Basin
Clear
None
1
1
1
No
No
No
Sentry Post
09/0212012
Basin
Clear
None
1
1
1
No
No
No
R-36
09/02/2012
Basin
Clear
None
1
1
1
No
No
No
• where 1 Is clear, 5 is very cloudy
:where 1 Is no solids, 5Is cwered with floating solids
• 'where 1 Indicates no solids, 5 Is extremely muddy
la .—Marrch Jnta
Outhll ID
Data
Structure
Color
Odor
•Ciarityl3-
5
••Floatin{Solids
I-5
•••Suspended Solids (I
5
Faam
OIIShean
Erosion or
De klon
racer Creek
Coffee Creek
002
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
003
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
004
2/19/2013
Basin
Clear
None
1
1
1
No
No
No
FBO
A
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
B
2/19/2013
Basin
Clear_
None
1
1
1
No
No
No
C
2/19/2013
Basin
Clear
None
1
1
1
No
No
No
D
2/18/2013
Basin
Clear
None
1
3
1
No
No
No
E
2/18/2013
Basin
Clear
None
1
I No
No
No
F
2/18/2013
Basin
Clear
None
1
1
1
No
Na
No
G
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
H
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
K
2/19/2013
Basin
Clear
None
I
1
1
No
No
No
I.T.
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
L
2/18/2013
Basin
clear
Nane
1
1
1
No
No
No
M
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
R
2/18/2013
Basin
Clear
None
1
I
1
No
No
No
Q
2/18/2013
Basm
Clear
None
1
1
1
No
No
No
RW23
2/18/2013
Basin
Clear
None I
1
1
1
No
No
No
Air Cargo
2/18/2013
Basin
Clear
None
1
1
1
No
No
No
Danga lake
2/18/2013
Basin
clear
None
1
1
1
No
No
No
Sent Post
2/18/2013
Basin
clear
None
1
1
I
No
No
No
R-36
2/18/2013
Basin
1 111
1
1
No
No
No
' where J. Is clear, 5 Is very cloudy
•where 1 Is no solids, 5 Is covered with floating solids
• 'where I Indicates no solids, 5Is extremely muddy
Aonl•luna 20U
Outldl ID
Data
Structure
Color
Odor
•Clarity (l-
sl
•'Floating Solids
1-s
•••Suspended'0hds �1
s
Foam
Oil Sheen
Ems no,
Deposition
Tier Creek
Coffee Creek
002
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
003
6/17/2013
Basin
Clear
None
E.6/17/2013
Basin
Clear
None
1
1
1
No
No
No
FBO
A
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
B
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
C
6/17/2013
Basin
Clear
None
1
I
1
No
No
No
D
6/17/2013
Basin
Clear
None
E
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
F
6/17/2013
Basin
Clear
None
1
3
1
No
No
No
G
6/17/2013
Basin
Clear
None
1
I
I
No
No
No
H
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
K
6/17/2013
Basin
Clear
None
K-Wert
1 6/17/2013
Basin
Clear
None
1
1
1
1 No
No
No I
L
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
M
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
R
6/17/2013
Basin
Clear
None
Q
6/17/2013
Basin
Clear
None
—�
RW23
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
Air Cargo
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
Danga Lake
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
Sentry Post
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
R-36
6/17/2013
Basin
Clear
None
1
1
1
No
No
No
• where 1 Is clear, 5Is very cloudy
-whom 1 Is no solids, 51s covered with floating solids
•••where 1 indicates no solids, 5 e extremely muddy
I. lv- Saohmhar 2013
Outfall ID
Data
Structure
Color
Odor
'Carity(1-
s
••Floatng Solids
1-5
•••Suspended Solid, 11
S
Foam
Oil Sheen
Eroabn or
De sition
Titer Creek
Coffee Creek
001
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
002
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
003
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
004
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
FBO
A
1 9/26/2013
Ditch
I Clear
None
1
1
1
No
No
No
B
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
C
9/26/2013
Ditch
Clear
None
I
1
1
No
No
No
D
9/26/2013
Basin
Clear
None
E
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
F
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
G
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
H
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
K
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
K-West
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
L
9/25/2013
Basin
Clear
None
M
9/26/2013
Basin
Clear
None
1
11
1
No
No
No
R
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
Q
9/26/2023
Basin
Clear
None
1
1
1
No
No
No
RW23
Air Cargo
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
Danga Lake
9/26/2013
Basin
Clear
None
1
1
1
No
No
Na
Sentry Post
9/26/2013
Basin
Clear
None
1
1
1
No
No
No
R-36
9/26/2013
Ditch
Clear
None
1
1
1I
No
No
No
• where 1 is dear, 5 is very cloudy
'-.here 1 Is no solids, 51s covered with floating solids
• •where 1 Indicates no solids, 51s extremely muddy
Outfall ID
Data
Structure
Color
Oder
'Clarity(1-
5(
••Floating Solids
1-5
•••Suspended Solids (I
s
Foam
ORSheen
Erosion or
Deposition
Tice, Creek
Coffee Creek
001
002
11/26/2013
Basin
Clear
None
I
1
I
No
No
No
003
11/26/2013
Basin
Clear
None
1
1
1
No
No
No
004
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
FBO
A
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
B
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
C
12/26/2013
Ditch
Clear
None
J.
1
1
No
No
No
D
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
E
11126/2013
Ditch
Clear
None
1
1
1
No
No
No
F
11/26/2013
Ditch
Clear
None
1
I
1
No
No
No
G
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
H
11/26/2013
Be,,.
Clear
None
1
1
1
No
No
No
K
11/26/2013
Basin
Clear
None
I
1
1
No
No
No
K-West
11/26/2013
Basin
Clear
None
1
1
1
No
No
No
L
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
M
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
R
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
Q
12/26/2013
Ditch
Clear
None
I
1
1
No
No
No
RW23
11/26/2013
Ditch
Clear
None
1
1
1
_
No
No
_
No
Au Cargo
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
Danga Lake
11/26/2013
Basin
Clear
None
1
1
]
No
No
No
Sen Post
11/26/2013
Basin
Clear
None
1
1
1
No
No
No
R-36
11/26/2013
Ditch
Clear
None
1
1
1
No
No
No
'•where 1 Is clear, 5 is very cloudy
:where 1 Is no solids, 51, covered with floating wilds
• 'where 1 Indicates no solids, 5 is extremely muddy
ww- s.aremh..2nta
Outhill ID
Data
Structure
Color
Odar
'Clar-ity(1-
S
•'Floating Solids
1-S
••'Suspended Solids (I
S
Foam
OII Shean
Erosion or
Deposition
Titer Creek
Coffee Creek
001
D02
9/24/2014
Ditch
Clear
None
1
1
1
No
No
No
003
9/24/2014
Ditch
❑ear
None
I
1
1
No
No
No
004
9/24/2014
Ditch
Clear
None
1
I
1
No
No
No
FBO
A
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
B
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
C
9/7/2014
Clear
None
1
1
1
No
No
No
D
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
E
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
F
9/24/2014
Ditch
Clear
None
1
1
1
No
No
No
G
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
G
9/24/2014
Ditch
Clear
None
1
1
1
No
No
No
H
9/2412014
Ditch
Clear
None
1
1
1
No
No
No
K
9/24/2014
Ditch
Clear
None
1
1
1
No
No
No
K-West
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
L
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
M
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
N
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
R
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
Q
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
RW23
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
Air Cargo
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
Danga Lake 1
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
Sentry Post
9/7/2014
Ditch
Clear
None
1
1
1
No
No
No
R-36
9/7/2014
Ditch
Clear I
None
1
I
1
No
No
No
• where 1 is clear, 5 is very cloudy
:where 1 Is no solids, 5 is covered with floating solids
• -where 1 Indicates no solids, 51s extremely muddy
Appendix E
Summary of Best Management Practices
BMP MATRIX
Storm Water Best Management Practices (BMPs) and Corresponding Target Activities
Charlotte/Douglas International Airport
Activity Description
Applicable BMP
1 2
3 4 5 6 7
8
9 10 11 12
13 14 15 16
17 18
A/V/E Deicing '
❑
■ ❑
❑
❑
AN/E Fueling
❑
■ ❑ ❑
❑
❑
❑
A/V/E Maintenance
❑ ■
❑ ❑
❑
❑
Aircraft Lavatory Service
❑
❑ ❑
❑ ■
❑
A/V/E Painting or Stripping
❑ ❑
❑
❑
❑
A/V/E Washing or Cleaning
❑
■ ❑
❑
❑
❑
Apron/Floor Washdown
❑ ❑
❑ ❑
❑ ❑ ■
❑
Cargo Handling
❑
❑
❑
❑
ChemicaVFuel Storage
❑
❑ ■
❑
❑
❑
❑
Equipment Storage
❑
❑
❑
Fire Equipment Testing
❑
❑
■
Pesticide/Herbicide Usage
❑
❑
■ ❑
❑
Potable Water Flushing
❑ ❑
❑
■
Runway Deicing
❑
❑
❑
❑ ■
Runway Rubber Removal I
❑
❑
■
Note: " A/V/E is the abbreviation for Aircraft/Vehicle/Equipment
❑ Indicates that BMP generally
applies
or relates to the activity ■ Indicates
that BMP is directed specifically
toward the activity
1: Elimination of Non -Storm Water Discharges to Storm Drain
6* Outdoor Waste and Material Handling
11: Lavatory Service Operations
16: Oil/Water Separators
2 Aircraft, Vehicle, and Equipment Maintenance
7: Outdoor Storage of Waste and Matenals
12 Outdoor Washdown/Sweeping
17: Emergency Spill Cleanup Plans
3* Aircraft, Vehicle, and Equipment Fueling
8: Waste/Garbage Handling and Disposal
13. Fire Fighting Foam Discharge
18* Airfield Pavement Deicing/Anti-icing
4: Aircraft, Vehicle, and Equipment Washing
9, Building and Grounds Maintenance
14, Potable Water System Flushing
5, Aircraft Deiang/Anti-Icing
10: Storm Water Pollution Prevention Education
15: Runway Rubber Removal
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-� - - _ - : - - . yyr .,�,t .,¢w'� _ _ • � ^ - _ - _ •;F . chi'• �', - , F; dot;• •- - '
71
- ,d�?P:; _ s�.' �''• y cam` a` _ _ _ , i., '.d._�..e;;' _ ;,iy ^f.; � �
BMP,1 n _ ..= `: r: ELIMINATION,:.O,F--'NON=STORMr,WATER
l.Yf a DISCHARG_ESTaSTORM-DRAIN; }
PURPOSE: TARGETED ACTIVITIES
Existing discharges: Eliminate non -storm water discharges to the storm
water collection system. Non -storm water discharges can be classified as
follows: 1) Activity -based (subtle), and 2) Overt (hard pipe connection).
Activity -based non -storm water discharges may include: wash water, and
spillage. Overt non -storm water discharges may include: process wastewater,
treated cooling water, and sanitary wastewater.
Prevention of illicit connections: Prevent improper physical connections to
the storm drain system from sanitary sewers, floor drains, industrial process
discharge lines, and wash racks through education, developing project
approval conditions, and performing both construction phase and post -
construction inspections.
GENERAL APPROACH:
Identification of Activity -Based (Subtle) Discharges:
The following techniques may be used to identify activity -based non -storm
water discharges to the storm water collection system:
■ Perform frequent activity inspections to identify non -storm water discharges
— stagger inspection times to cover all work periods.
■ Perform visual inspections of discharge points to the storm drain system —
observe uncharacteristic volumes, colors, turbidity, odors, deposition,
staining, floatables, and foaming characteristics of any flow.
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Perform inspections during the design review and project construction
phases to ensure drainage, wastewater, and water supply connections are
correct (no cross connections or illicit hookups).
■ Develop a set of as -built prints for all projects. Keep a set of the prints at
the facility.
■ Design projects to include adequate waste repositories at locations near
waste origin points.
■ Provide adequate and appropriately designed facilities for functions such
as steam cleaning, degreasing, painting, mechanical maintenance,
chemical/fuel storage and delivery, material handling, waste handling and
storage, lavatory service, and food preparation.
< All activities with potential
to impact storm water
TARGETED POLLUTANTS
< Oil and Grease
< Antifreeze
< Fuel
< Solvent/Cleaning -
Solutions
< Battery Acid
< Pesticides/Herbicides/
Fertilizers
< Paint
< Aircraft Fire Fighting
Foam (AFFF)
< Scrap Metal and Parts
< Garbage and Hazardous
Waste
< Sediment
< Landscape Waste
< Fooatables
< Lavatory Chemicals and
Waste
< Potable Water System
Cleaning Chemicals
< Rubber Particles
KEY APPROACHES
< Perform inspections and
enforcement
< Provide training for
employees
< Promote education of
vendors/public
BMP01.doc BMP1-1
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APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
■ Use "dry" cleaning and surface preparation techniques where feasible.
■ Limit the availability of outdoor water supplies (hose bibs).
■ Post signs at outdoor water sources stating the appropriate uses and discouraging uses that would
introduce pollutants to the storm drain system/receiving waters.
Contingency Response
■ Develop and implement a Spill Prevention Control and Countermeasure (SPCC) Plan, if required
under guidelines set forth in 40 CFR, Section 112.3(a), (b).
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
Inspection and Training
■ Inspect waste containers frequently for leaks and proper closure seal.
■ Develop employee training programs which emphasize the proper disposal procedures for
operations -derived wastes.
■ Provide the appropriate level of employee training in the following areas: spill response and
prevention, storm water pollution prevention education (see SC-10 for storm water pollution
education approaches), right -to -know awareness training, and hazardous materials management.
REQUIREMENTS:
■ Capital and O&M may be required to eliminate non -storm water discharges.
LIMITATIONS:
i Storm drain documentation for many facilities is not up-to-date.
i Activity -based (subtle) non -storm water discharges from a particular facility are typically sporadic,
transient, and often require frequent inspections to detect.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
BMP01.doc BMP1-2
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EQUIPMENT:MAINTEN�AN.CE'�'_����,<<,�3 .;
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.: .. -..,.. -. �_ , .: -' =ice<, ia•;. s � . i � .. • _ - " _ _ - -
PURPOSE:
Prevent or reduce the discharge of pollutants to storm water from aircraft,
vehicle, and equipment maintenance and repair, including ground vehicle and
equipment painting/stripping and floor washdowns.
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Provide covered maintenance areas when designing new facilities or
upgrading existing facilities. Utilize indoor areas, lean-tos, or portable
covers.
■ Locate outdoor maintenance areas so minimal quantities of runoff cross
the site.
■ Include appropriate storm water quality structures (oil/water separators,
sumps, first flush diversion basins, etc. - see TC-1 for further information
regarding treatment control BMPs) in the design of outdoor maintenance
areas.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
Implement the following to the maximum extent practicable.
Good Housekeeping
■ Use drip pans.
■ Use absorbent materials at potential problem areas. Adequately
collect/remove absorbent materials from area after use and dispose of
them in an appropriate manner.
■ Drain and crush oil filters (and oil containers) before recycling or disposal.
Store crushed oil filters and empty lubricant containers in a leak -proof
container - cover if outdoors.
■ Label storm drain inlets to indicate they are to receive no wastes. Do not
hose down work areas to the storm drainage system or use concrete
cleaning products unless the storm drain inlet is blocked and wash water is
collected and properly disposed of through a permitted sewer connection.
As an alternative, use mops, dry sweeping compound, or contract
professional cleaning services. Confirm the use of appropriate disposal
practices by contract cleaning services.
■ Drain and properly dispose of all fluids and remove batteries from salvage
aircraft, vehicles, and equipment.
■ Drain parts and equipment of all fluids. Store on secondary containment
under cover.
TARGETED ACTIVITIES
< Aircraft/Vehicle/
Equipment
Maintenance
< Aircraft/Vehicle/
Equipment Painting or
Stripping
< Apron/Floor Washdown
< Potable Water System
Cleaning
TARGETED POLLUTANTS
< Oil and Grease
< Vehicle Fluids
< Solvents/Cleaning
Solutions
< Fuel
< Battery Acid
< Paint
KEY APPROACHES
< Conduct maintenance
indoors, or in covered
area.
< Prevent wash water
discharges to the storm
drain
< Clean catch basins
regularly
< Collect and properly
dispose of all fluids
BMP02.doc BMP#2-1
HAR'GLOTTE/DOU.GLAS,INTERNATI.O_ NAL_ AIRPORT ti:T j
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.-EQUIPMENT.;MAINTENANCE.A:'
al -
Good Housekeeping, cont.
■ Recycle or properly dispose of the following: grease, oil, antifreeze, brake fluid, cleaning solutions,
hydraulic fluid, batteries, transmission fluid, and filters.
■ Use biodegradable products and substitute materials with less hazardous properties where feasible.
Physical Site Usage
■ Where feasible, move maintenance activities indoors or provide cover over work area.
■ Use designated washing, steam cleaning, and degreasing areas to clean equipment.
■ Store mechanical parts and equipment that may yield even small amounts of contaminants (e.g., oil or
grease) under cover and away from drains.
Structural Controls
■ Equip maintenance and cleaning areas with runoff controls that prevent discharge to storm sewers.
■ Install and maintain catch basin filter inserts that assist in the removal of oil and grease, sediments and
floatables.
Maintenance
■ Maintain clean equipment by eliminating excessive amounts of external oil and grease buildup. Use
water -based cleaning agents or non -chlorinated solvents to clean equipment.
■ Regularly clean any catch basins which receive runoff from a maintenance area, especially after larger
storms.
■ Inspect, clean and maintain sump and oil/water separators, if necessary.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
■ Furnish all maintenance vehicles with adequate supplies of spill response materials and appropriate
spill response procedures.
Inspection and Testing
■ Provide the appropriate level of employee training in the following areas: spill response and prevention,
storm water pollution prevention education (see SC-10 for storm water pollution education approaches),
right--to-know awareness training, and hazardous materials management.
■ Provide employee storm water quality awareness training.
■ Develop regular maintenance and inspection programs for oil/water separators.
■ Characterize wastes collected from oil/water separators. Provide appropriate employee training.
REQUIREMENTS:
■ Capital investment may be required depending on the facility layout. In some cases, diversion basins
may be required.
%E O&M investment is not expected to be significant.
BMP02.doc BMP#2-2
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LIMITATIONS:
• Size, space and time limitations may preclude work from being performed indoors.
• Identification of engine and equipment leakage points may require the use of solvents or other cleaners
to remove external accumulations of oily grime.
RELEVANT RULES AND REGULATIONS:
* FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
* 40 CFR 110.3 Discharge of Oil
* 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
* 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
* 40 CFR 401 Effluent Limitation Guidelines
BMP02.doc BMP#2-3
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PURPOSE:
TARGETED ACTIVITIES
Prevent fuel spills and leaks, and reduce their impacts to storm water.
< Aircraft/Vehicle/
Equipment Fueling
< Taking pre-flight AVGAS
APPROACH TO FUTURE FACILITIES AND UPGRADES:
fuel samples
Design of New Facilities and Existing Facility Upgrades
< Apron/Floor Washdown
■ Design fueling areas to prevent the run-on of storm water and the runoff of
spills by employing the following approaches:
TARGETED POLLUTANTS
- Cover the fueling area if possible.
< Fuel
- Use a perimeter drain or slope the fueling area to a dead-end sump or
oil/water separator.
- Pave the fueling area with concrete rather than asphalt.
KEY APPROACHES
■ If storm water runoff from fueling areas is not collected, install an
< Install berms or curbing
appropriately -sized oil/water separator. Regulatory agency approvals are
around fueling areas
required.
< Use absorbent materials
■ Install and maintain vapor recovery systems where required and/or
and/or vacuum equipment
appropriate.
for spills
< Install proper equipment
■ Existing underground fuel storage tanks should be upgraded with leak
for fuel dispensing and
detection, spill containment, and overfill protection in advance of December
tank monitoring to prevent
22, 1998, the federal regulatory deadline. This is relevant to storm water
spills, leaks and overflows
regulations due to the potential for contamination of surface soils or waters
< Use CATS JARS to take
that could be transported by storm water runoff.
AVGAS fuel samples;
■ Design facilities to include secondary containment where required and/or
dispose of samples at
appropriate.
collection sites; use fire -
rated containers for
storage of fuel samples
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
Implement the following to the maximum extent practicable.
Good Housekeeping
■ Fuel pumps intended for vehicular use (not aircraft) should be posted with
signs stating "No Topping Off" to prevent overflow.
■ Use absorbent materials and spot cleaning for small spills; do not hose
down the area unless the storm drain is blocked and drainage is collected
by vacuum truck and disposed of through a permitted connection to the
sanitary sewer.
■ Properly dispose of any fuel spills and leaks. Vacuum equipment/trucks
are recommended for collection. Always dispose of materials in an
approved manner; use an approved treatment facility through a permitted
connection. Never discharge materials to a catch basin or storm drain.
BMP03.doc BMP#3-1
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Good Housekeeping (contd.)
■ Use pigs/mats over catch basins during fueling activity.
■ Manage the disposal of water that collects in fuel tanks and fueling hydrant sumps according to state
and federal regulations.
Physical Site Usage
■ Avoid mobile fueling of equipment wherever feasible; fuel equipment at designated fueling areas.
Structural Controls
■ Cover the fueling area if possible.
■ Divert storm water runoff away from fueling area to avoid storm water contact with contaminated
surfaces through the use of berms or curbing.
■ Install gate valves at catch basins for use during fueling activity.
■ Employ secondary containment or cover when transferring fuel from a tank truck to a fuel tank.
Equipment
■ Provide appropriate monitoring for tanks containing fuel, such as:
- Level indicators and gauges.
- Overfill protection with alarms.
- Interstitial leak detection for double -walled tanks.
- Routine inspection/lockout for drainage valves for tank containment areas.
■ Fuel dispensing equipment should be equipped with "breakaway" hose connections that will provide
emergency shut -down of flow should the fueling connection be broken through movement.
■ Automatic shut-off mechanisms should be in place on fuel tankers. These valves should remain in the
closed position unless manually opened during fueling.
■ Use GATS JARS for collecting AVGAS fuel samples, which enables clear and bright fuel to be returned
to the aircraft fuel tank.
Maintenance
■ Inspect, clean and maintain sumps and oil/water separators at appropriate intervals.
Contingency Response
■ Develop and implement a Spill Prevention Control and Countermeasure (SPCC) Plan if required under
guidelines set forth in 40 CFR, Sections 112.3(a), (b).
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
■ Furnish adequate spill response information, equipment and materials on all fueling vehicles.
Inspection and Training
■ Inspect fueling areas and storage tanks regularly. Record all maintenance activities and inspections
relating to fueling equipment and containers in a log book.
■ Underground fuel storage tanks should be tested as required by federal and state laws.
i Provide the appropriate level of spill response training to personnel to address all types of spills.
BMP03.doc BMP#3-2
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REQUIREMENTS:
■ In rare cases, a fueling area may need to be retrofitted to minimize storm water contamination.
Generally, practical design concepts, such as incorporating extruded curb along the upstream side of
facilities to prevent run-on of storm water, will be appropriate.
■ All AVGAS fuel samples should be collected and disposed of at collection sites, or stored in fire -rated
containers.
LIMITATIONS:
■ Properly sized and installed oil/water separators must be regularly maintained to be effective (see TC-1
for a description of management practices relating to oil/water separator operations and maintenance).
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC OPA/Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharge
• 40 CFR 401 Effluent Limitation Guidelines
BMP03.doc BMP#3-3
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BMP#r4AIRCRAFT"VEHICLE:AND�E'QUIP:MENT'WASHING�F�����`
CLEANING ANDDEGREASING
PURPOSE:
Prevent or reduce the discharge of pollutants to storm water drains from aircraft,
vehicle, and equipment washing, and cleaning and degreasing activities.
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Use off -site commercial washing where feasible. Using appropriate off -site
facilities will decrease the potential for storm water pollution on -site.
■ Evaluate the need for incorporating a wash water recycling system into the
project design.
■ Outdoor washing operations should have the following design characteristics:
- Paved with portland cement concrete (PCC).
- Bermed and/or covered to prevent contact with storm water.
- Sloped to facilitate wash water collection.
- Wash water should be collected in a dead-end sump for removal or
discharged to the sanitary sewer through a permitted connection.
- Discharge piping serving uncovered wash areas should have a positive .
shut-off control valve that allows switching between the storm drain and
the sanitary sewer.
- Wash areas should be clearly identified with appropriate signage.
- Equipped with an oil/water separator designed to operate under storm
water runoff conditions to treat storm water volumes and flow rates.
(Regulatory agency approvals are required.)
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
Implement the following to the maximum extent practicable.
Good Housekeeping
■ Use "dry" washing and surface preparation techniques when possible.
Consider dry washing as an option regardless of aircraft size. Remove all
materials (i.e., drippings and residue) using vacuum methods. Dispose of
properly.
■ Provide secondary containment, and cover if possible, for containers of
washing and steam cleaning additives.
■ Use pigs/mats to control the discharge of wash water.
■ Use biodegradable phosphate -free detergents.
■ Keep wash area clean and free of waste.
■ Include proper signage to prohibit the discharge of waste oils into the drains.
■ Collect and discharge wash water to an approved treatment facility (sanitary
sewer system) through a permitted connection.
■ Keep degreasing activities in a fully enclosed area, if possible, located away
from storm drains.
■ Properly dispose of cleaning/degreasing waste.
TARGETED ACTIVITIES
< Aircraft/Vehicle/
Equipment Painting or
Stripping
< Aircraft/Vehicle/
Equipment Washing or
Cleaning
TARGETED POLLUTANTS
< Oil and Grease
< Solvent
< Vehicle Fluids
< Cleaning Solutions
KEY APPROACHES
< Use designated area
< Use dry washing
techniques
< Recycle wash water or
discharge appropriately
< Cover catch basins
< Provide training
BMP04.doc BMP#4-1
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S:PLEANING AND. DEGREASING
Physical Site Usage
■ Use off -site commercial washing and steam cleaning where feasible. Using appropriate off -site facilities
will decrease the potential for storm water pollution on -site.
■ Use designated wash areas that are covered and/or bermed to prevent contamination of storm water by
contact with wastes.
Structural Controls
■ Gate valves at catch basins will prevent discharge to the storm drainage system during washing activities
by facilitating the collection of wash water.
■ Filter and recycle wash water when possible.
Maintenance
■ Patch and repair berms and PCC to maintain containment system.
■ Inspect, clean, and maintain sumps, oil/water separators, and on -site treatment and recycling units.
Management
■ File a Wash Plan for approval by the Aviation Department prior to commencing wet washing activities in
any area outside designated wash rack.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near areas
where spills of cleaning chemicals may be likely to occur.
Inspection and Training
■ Provide the appropriate level of employee training in the following areas: spill response and prevention,
storm water pollution prevention education (see SC-10 for storm water pollution education approaches),
right -to -know awareness training, and hazardous materials management.
■ Develop regular maintenance and inspection programs.
■ Characterize wastes derived from oil/water separators. Provide appropriate employee training.
REQUIREMENTS:
■ Capital costs vary depending on measures implemented.
- LOW COST: $500-1,000 for berm construction.
- MEDIUM COST: $5,000-20,000 for plumbing modifications (including re-routing discharge to the
sanitary sewer and installing a simple sump).
- HIGH COST: $30,000-150,000 for on -site treatment and recycling.
■ O&M costs increase with increasing capital investment.
LIMITATIONS:
■ Some POTWs may require pretreatment and monitoring of wash water discharges to the sanitary sewer.
■ Steam, cleaning and de -greasing operations can generate significant pollutant concentrations that may
require permitting, monitoring, pretreatment, and inspections.
BMP04.doc BMP#4-2
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RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
BMP04.doc BMP#4-3
AIRCRA
PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water from aircraft deicing
Aircraft Deicing or Anti -
and anti -icing procedures.
icing
APPROACH TO FUTURE FACILITIES AND UPGRADES:
TARGETED POLLUTANTS
Design of New Facilities and Existing Facility Upgrades
Ethylene glycol
• Consider requirements in future USEPA Airport Deicing Effluent Guidelines
Propylene glycol
Additives
• When designing or modifying operating areas, consider incorporating the
following features and characteristics:
- Clearly designated deicing areas
KEY APPROACHES
- Ramp pavement sloped to facilitate containment/collection of deicing runoff
* Deice in designated areas
- Isolation of drainage during deicing operations using catch basin blocks,
only
inline gate or diversion valves, or sewer balloons to facilitate collection of
e Apply only required
deicing runoff
amounts of fluid to
- Collection of isolated deicing runoff
maintain flight safety
• Evaluate alternatives for appropriate storage and disposal (treatment or
e Collect deicing runoff from
recycling) of collected runoff.
ramp area when done
• Conduct mass balance monitoring for aircraft deicers to provide collection
o Properly handle and
dispose of collected
performance data on new and upgraded facilities.
deicing runoff
• Evaluate collection performance of deicing pads annually. Address any
deficiencies prior to the next deicing season.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
• Consider environmental characteristics of products when selecting SAE -
certified deicing and anti -icing fluids appropriate to aircraft and operating
conditions '
• Employ application technologies and methods that minimize the volumes of
deicers and anti-icers required to ensure the safe operation of the aircraft
• Perform deicing and anti -icing operations only in designated areas
• Collect impacted runoff from ramp surfaces following deicing/anti-icing
operations. Wet -type sweepers may be effective in collecting deicing runoff.
• Dispose of collected runoff in accordance with local, state, and federal
regulations
Contingency Response
• Fill deicing trucks in areas where spillage will be contained.
• Provide for containment of leakage from deicing trucks and deicer storage
BmPosdvu BMP#5'1
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Inspection and Training
Monitor deicing and anti -icing operations regularly to ensure quantities of fluids used are optimized for
maintaining aircraft safety while minimizing runoff.
Provide the appropriate level of employee training in the following areas: implementation of methods
and technologies to optimize deicer and anti-icer application, areas designated for aircraft deicing/anti-
icing, collection and disposal of deicing runoff, spill response and prevention, and storm water pollution
prevention education.
REQUIREMENTS:
• Deicing and anti -icing fluid application techniques must be consistent with the aircraft operator's FAA -
approved snow and ice control plan
• An appropriate method for disposing of collected deicing runoff is essential if collection is implemented
• Costs associated with collection and proper disposal of deicing runoff can be high
LIMITATIONS:
• Weather conditions limit the applicability of certain techniques for reducing deicer and anti-icer usage
• Aircraft operators may have limited flexibility in selecting aircraft deicing and anti -icing products
• Effective and efficient collection of deicing runoff requires favorable infrastructure features and suitable
equipment
• POTW may refuse to accept deicing chemicals, such as ethylene and propylene glycol, in discharges to
the sanitary sewer system, or may require extensive control and monitoring of deicing runoff discharges
to the sanitary sewer.
RELEVANT RULES AND REGULATIONS:
• North Carolina General Statute 143-215.1
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 401 Effluent Limitation Guidelines
BMP05.doc BMP#5-2
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BMP#6
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PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water from handling
< Aircraft/Vehicle/
potential pollutants outside enclosed buildings.
Equipment Deicing
< Aircraft/Vehicle/
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Equipment Fueling
Design of New Facilities and Existing Facility Upgrades
< Aircraft/Vehicle/
■ Design outdoor waste and material handling areas to prevent storm water run-
Equipment Maintenance
< Aircraft Lavatory Service
on through the use of the following practices:
< Cargo Handling
- Grading or berming
< Fuel/Chemical Storage
- Positioning roof downspout to direct storm water away from outdoor waste
< Pesticide/Herbicide
and material handling areas
Usage
■ Design facilities so that materials which may contribute pollutants to storm
< Runway Deicing
water may be stored indoors or under cover.
■ Incorporate oil/water separators into exposed loading dock designs.
TARGETED POLLUTANTS
<
Fuel
APPROACH TO EXISTING FACILITY ACTIVITIES:
<
Pesticides and Herbicides
Operational Considerations
<
Oil and Grease
Good Housekeeping
<
Solvent/Cleaning
■
Use seals or door skirts between vehicles and structures to prevent material
<
Solutions
Battery Acid
exposure to rainfall.
<
Lavatory Chemicals and
■
Contain and adsorb leaks during transfers and spillage from hose
Waste
disconnections; dispose of residue properly.
<
Deicing Chemicals
■
Avoid transferring or using materials in close proximity to storm drain inlets.
Cover nearby storm drain inlets during material transfer or use.
KEY APPROACHES
■
Use drip pans to contain small releases and promptly clean and remove drip
<
Conduct loading/
pans when not in use.
unloading under cover
■
Transfer and use liquids only in paved areas. Portland cement concrete
<
Transfer materials in
(PCC) should be used if the liquid is asphalt reactive.
paved areas, away from
■
Provide contractors and haulers with copies of pertinent BMPs. Require
storm drain inlets
contractor/hauler adherence to BMP specifications.
<
Contain and absorb
■
Consider contracting maintenance operations for material handling
<
releases
Maintain readily
equipment. Designate an appropriate area for contractors to perform
accessible spill kits
maintenance activities. Verify proper waste disposal practices of contractors.
<
Immediately place waste
and materials in proper
Physical Site Usage
storage/disposal location.
■
Protect all loading/unloading activities and material use areas from rainfall,
run-on and wind dispersal to the maximum extent practicable. Viable options
include conducting activities under existing cover, or moving indoors.
■
Position tank trucks or delivery vehicles so that possible spills or leaks can be
contained.
■
Provide appropriate spill containments, hand pumps, and other devices to
minimize releases during material transfer.
BMP06.doc BMP#6-1
2 , o CHARL TTE%D
r O° ,OUGLAS 'INTERNAT10NAL AI;R_21P.ORT .
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Structural Controls
■ Cover loading/unloading areas/docks and material use areas to reduce exposure of materials to rain.
Construct roofing structures over material handling areas, or move indoors.
■ Investigate feasibility of relocating storm drain inlets away from fuel hydrants.
Maintenance
■ Inspect loading/unloading areas and material use areas for repair and patching.
■ Inspect, clean and maintain oil/water separators.
Contingency Response
■ Maintain adequate supplies of spill response equipment in accessible locations near areas where spills
may be likely to occur.
■ Include spill kits on appropriate material handling vehicles and equipment.
Inspection and Training
■ Conduct regular inspections and make repairs as necessary.
■ Check loading/unloading equipment (valves, pumps, flanges, and connections) regularly for leaks.
■ Develop and implement a written operations plan which describes loading/unloading procedures.
■ Provide proper training for material handling equipment operators.
■ Provide the appropriate level of employee training in the following areas: spill response and prevention,
storm water pollution prevention education (see BMP#10 for storm water pollution education
approaches), right -to -know awareness training, and hazardous materials management.
REQUIREMENTS:
■ Capital and O&M costs should be low except when covering large loading/unloading areas.
LIMITATIONS:
■ Space and time limitations may preclude the indoor or covered transfer of cargo and materials.
RELEVANT RULES AND REGULATIONS:
• FIR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm water Discharges
BMP06.doc BMP#6-2
SE" 0__HARL0_TTE/QQUGLA INTERNATIONAL'AIRR.
.4; iVic•f 7�
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--.BMP#I,
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40,MAIE-RIALS.
-,OUTDOOR _QRAP!�-,OF
PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water from outdoor .
< Aircraft/Vehicle/
storage areas for waste or material (e.g., fuel, chemicals, bagged solids,
Equipment Fueling
contaminated soil, bulk storage, etc.)
< Aircraft/Vehicle/
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Equipment Maintenance
< Aircraft Lavatory Service
Design of New Facilities and Existing Facility Upgrades
< Aircraft/Vehicle/
• Require the use of appropriate water quality control structures for fuel,
Equipment Washing or
waste, and chemical storage areas such as berms, detention/retention
Cleaning
basins, and sumps. Develop appropriate minimum performance
< Fuel/Chemical Storage
standards for these water quality control structures and implement a
< Equipment Storage
reporting program to monitor the performance and maintenance of
these structures.
TARGETED POLLUTANTS
• Chemical, fuel, and oil dispensing (non -aircraft) sites, and waste
collection areas should be covered, if possible.
< Fuel
< Solvent
• Chemical, fuel, and oil dispensing sites, and waste collection areas
< Cleaning Solutions
should be sloped to contain releases.
< Liquid Wastes
• Develop standard guidelines for the management of storm water which
< Lavatory Chemicals/
collects in secondary containment areas.
Waste
APPROACH TO EXISTING FACILITY ACTIVITIES:
KEY APPROACHES
Operational Considerations
Good Housekeeping
< Store materials in a
• Avoid dispensing from drums positioned horizontally in cradles.
covered or fully enclosed
Dispensing materials from upright drums equipped with hand pumps is
area
< Provide secondary
preferred. Always use secondary containment and self closing spigots
containment
if dispensing from horizontally positioned drums.
< Implement an SPCC, if
• Store drums and containers on spill containment pallets or other
required
structures to keep the container out of contact with storm water.
< Perform and document
• Use drum lids and drum -top absorbent pads to prevent rainfall from
periodic inspections
washing materials and drippage from the top of containers to the storm
drain system.
• Discharge collected storm water from secondary containment areas
according to guidelines developed by the federal government and
applicable state and local regulations.
• Store all materials in their original containers or containers approved
for that use. Ensure that all containers are appropriately sealed. Store
empty containers in fully enclosed areas, under cover, or move them
off -site.
• Properly label all chemical containers with information, including their
contents, hazards, spill response and first aid procedures,
manufacturer's name and address, and storage requirements.
Maintain copies of MSDS on file for any materials stored and/or
handled by the applicator.
• Maintain a spill response plan near the material or waste storage area.
BMP07.doc BMP#7-1
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BMP#7:_ OUTDOOR-STORAGE-'_OF11V'ASTE ANDf,MATERI'ALS
Physical Site Usage
■ Protect all significant materials from rainfall, run-on, runoff and wind dispersal to the maximum
extent practicable. Viable options are:
- Store material in a fully enclosed area.
- Cover an outdoor storage area with a roof or awning.
Cover the material with a temporary covering made of polyethylene, polypropylene, or hypalon.
Minimize storm water run-on by enclosing the area, building a berm around the area, storing
indoors, or completely cover the stored material.
■ Reduce the quantities of material and waste stored outside (i.e., chemicals) to the minimum volume
required based on variables such as release potential, usage, and shelf life.
■ Make use of existing overhangs as covered storage areas.
Structural Controls
■ Provide berms or secondarily contain storage tankers, ASTs, drums and containers.
■ Install and maintain catch basin filter inserts.
Maintenance
■ Inspect, clean and maintain sumps, if applicable.
Contingency Response
■ Develop and implement a Spill Prevention Control and Countermeasure (SPCC) Plan, if required
under guidelines set forth in 40 CFR, Section 112.3(a), (b).
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
■ Post signs at all chemical storage locations in clearly visible locations noting the materials stored,
emergency contacts, and spill cleanup procedures.
Inspection and Training
■ Provide the appropriate level of employee training in the following areas: spill response and
prevention, storm water pollution prevention education (see BMP#10 for storm water pollution
education approaches), right -to -know awareness training, and hazardous materials management.
■ Perform and document periodic inspections in a log book. Inspection items should include the
following:
- Check containers for external corrosion and structural failure.
- Check for spills and overfills due to operator failure.
- Check for failure of piping system (pipes, pumps, flanges, couplings, hoses, and valves).
- Check for leaks or spills during pumping of liquids or gases.
- Visually inspect new tanks or containers for loose fittings, poor welds, and improper or poorly
fitted gaskets.
- Inspect tank foundations and storage area coatings.
BMP07.doc BMP#7-2
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REQUIREMENTS:
■ Capital and O&M costs will vary widely depending on the size of the facility and the necessary
controls. Costs associated with on -site detention/retention facilities could be high.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995-Multi-Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
• 40 CFR 260 et. seq. Identification and Listing of Hazardous Waste
BMP07.doc BMP#7-3
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PURPOSE:
Prevent or reduce the discharge of pollutants to storm water from waste
handling and disposal by tracking waste generation, storage, and proper
disposal; reducing waste generation and disposal through source reduction,
re -use, and recycling; and preventing run-on and runoff from waste
management areas, including garbage collection areas.
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Avoid the following characteristics when examining candidate sites for
storing wastes:
- Excessive slope
- High water table
- Locations near storm drain inlets
- Locations near public access areas
■ Waste handling and storage areas should be covered, if possible.
■ Develop standard guidelines for the management of storm water that
collects in secondary containment areas.
■ Incorporate sanitary sewer drains into bermed, outdoor, non -hazardous
waste storage areas, if approved by the local wastewater treatment
agencies/regulations.
■ Provide contained (and covered, if possible) area for hazardous waste
collection sites.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
Good Housekeeping
■ Perform regular housekeeping to maintain waste storage areas in a
clean and orderly condition.
■ Recycle materials whenever possible.
■ Inspect waste management areas for spills and waste management
containers for leaks.
■ Ensure that sediments and wastes are prevented from being washed,
leached, or otherwise carried off -site.
■ Completely drain containers (e.g., quart oil cans) prior to disposal in trash
receptacles.
■ Eliminate waste collection piles (i.e., "boneyards").
TARGETED ACTIVITIES
< Aircraft/Vehicle/
Equipment Maintenance
< Aircraft/Vehicle/
Equipment Painting or
Stripping
< Fuel/Chemical Storage
< Garbage Collection
TARGETED POLLUTANTS
< Oil and Grease
< Vehicle Fluids
< Solvents/Cleaning
Solutions
< Dumpster Wastes
KEY APPROACHES
< Cover waste storage
areas
< Recycle materials
< Regularly inspect and
clean waste storage
areas
< Berm waste storage
areas to prevent contact
with run-on or runoff
< Perform dumpster
cleaning in designated
areas
< Properly dispose of all
fluids
BMP08.doc BMP8-1
' CHARLOTTE/DOUGLAS'INTERNATIONAL:AIRPORT z
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Good Housekeeping (contd)
■ Schedule waste pickup as frequently as necessary to keep storage of waste to a minimum and to
avoid overloaded/overfilled disposal containers.
■ Minimize spills and fugitive losses such as dust or mist from loading areas.
■ Maintain a minimal inventory of required chemicals to reduce the magnitude of potential spills and limit
waste generation.
■ Track waste generation:
- Characterize waste streams.
- Evaluate the process generating the waste for pollution prevention opportunities.
- Maintain accurate information on waste streams using: manifests, bills of lading, biennial reports,
permits, environmental audits, SARA Title III reports, emission reports, Material Safety Data
Sheets (MSDS), NPDES discharge monitoring reports, inventory reports, data on chemical spills,
and emissions data.
■ Find substitutes for harmful chemicals.
■ Properly dispose of unusable chemical inventory.
Physical Site Usage
■ Segregate and separate wastes.
■ Avoid locating waste handling and storage in areas with storm drain inlets/catch basins.
■ Locate waste storage areas beneath existing cover, if possible.
Structural Controls
■ Enclose or berm waste storage areas, if possible, to prevent contact with run-on or runoff.
Garbage Collection Areas
■ Design facilities to provide shelter and secondary containment for dumpsters.
■ Use covered dumpsters and keep them closed and locked.
■ Use only dumpsters with plugged drain holes to prevent leaks from waste materials.
■ Do not dispose of liquid wastes such as oils or hazardous materials into dumpsters. Completely drain
liquid waste containers prior to disposal.
■ Perform dumpster cleaning in designated areas that are bermed to contain wash water for a
subsequent disposal or discharge to the sanitary sewer. Ramp scrubbers are effective in removing
wash water from paved areas. Dispose of or recycle all fluids collected.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
■ Equip waste transport vehicles with spill containment equipment.
BMP08.doc BMP8-2
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WASTPJGARBAGE, HANDLING AND DISPOSAL°
Inspection and Training
■ Provide the appropriate level of employee training in the following areas: spill response and prevention,
storm water pollution prevention education (see BMP#10 for storm water pollution education
approaches), right -to -know awareness training, and hazardous materials management.
■ Performand document in a log book periodic inspections of hazardous and non -hazardous waste
storage areas. Inspection items should include the following:
- Check containers for external corrosion and structural failure.
- Check for spills and overfills due to operator failure.
- Check for failure of piping system (pipes, pumps, flanges, couplings, hoses, and valves).
- Check for leaks or spills during pumping of liquids or gases.
- Visually inspect new tanks or containers for loose fittings, poor welds, and improper or poorly fitted
gaskets.
- Inspect tank foundations and storage area coatings.
- Inspect dumpster areas for signs of leakage.
REQUIREMENTS:
■ Capital and O&M costs for these programs will vary substantially depending on the size of the facility
and the types of wastes handled.
LIMITATIONS:
■ Hazardous waste that cannot be re -used or recycled; must be disposed of at a permitted facility by a
licensed hazardous waste hauler.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995-Multi-Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
• 40 CFR 260 et. seq. Identification and Listing of Hazardous Waste
BMP08.doc BMP8-3
CHARLOTTE%DOUGLAS ,INTERNATIONA ,AIRPORT';
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S TENANCr`k•r _P#9
BBUILDINGYANDGOD
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PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water from building
< Building Maintenance
and grounds maintenance by washing and cleaning up with as little water as
< Grounds Maintenance
possible, preventing and cleaning up spills immediately, keeping debris from
< Pesticide/Herbicide Use
entering storm drains, and maintaining the storm water collection system.
< Outdoor Washdown
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Incorporate areas of landscape into project design. Landscape areas
are pervious and will result in less runoff discharge from a site.
■ Incorporate design considerations such as leaving or planting native
vegetation to reduce irrigation, fertilizer, and pesticide needs.
■ Select landscaping plants that require little maintenance and/or pest
control.
■ Incorporate storm water detention/retention to reduce peak runoff flows
and for water quality control.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
Good Housekeeping
■ Collect outdoor washdown water and properly dispose of it through a
permitted connection to the sanitary sewer. Approval from treatment
facility required for discharge.
■ Clean any catch basins that receive runoff from maintenance areas on
a regular basis. Use a vacuum truck to remove accumulated
materials. Do not flush wastes into the storm drain system.
■ Minimize use of pesticides, herbicides, and fertilizers. Use according to
directions. Seek less harmful/toxic products to replace ones currently
used.
■ Utilize integrated pest management where appropriate.
■ Properly dispose of landscape waste, wash water, sweepings, and
sediments.
■ Regularly clean paved surfaces that are exposed to industrial activity.
Use "dry' cleaning techniques, such as sweeping, whenever possible.
TARGETED POLLUTANTS
< Pesticides/Herbicides/
Fertilizers
< Oil and Grease
< Sediment
< Landscape Waste
< Washdown Waste
< Building Maintenance
Materials (paint, roofing,
etc.)
KEY APPROACHES
< Keep paved surfaces
cleaned and swept
< Clean catch basins
regularly using vacuum
trucks
< Manage use of
pesticides/herbicides/
fertilizers
BMP09.doc BMP#9-1
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Structural Controls
■ Provide landscaped areas where erosion is becoming a problem.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may occur.
Inspection and Training
■ Provide the appropriate level of employee training in the following areas: spill response and
prevention, storm water pollution prevention education (see BMP#10 for storm water pollution
education approaches), right -to -know awareness training, and hazardous materials management.
REQUIREMENTS:
■ Costs will vary depending on the type and size of the facility. Costs of on -site storm water
detention/retention facility could be high.
LIMITATIONS:
■ Alternative pest/weed controls may not be available, suitable, or effective in every case.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substances
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
BMP09.doc BMP#9-2
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PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water through
< All Activities with Potential to
implementing an education program targeting employees, contractors,
Impact Storm Water
vendors, and the public.
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Work early on with design and construction engineers, and local storm
water authorities to incorporate proactive storm water management
features into projects such as decreased impervious areas, infiltration
BMPs, biofilters, oil/water separators, etc.
■ Inform all construction contractors of their responsibility to comply with
adopted BMPs and with regulations prohibiting cross connections
between sanitary sewers and storm drains. Provide contractors and
subcontractors with copies of relevant BMPs during specification and
bidding phases.
I
APPROACH TO EXISTING FACILITY ACTIVITIES:
Contingency Response
■ Provide adequate implementation training for facilities with a Spill
Prevention Control and Countermeasure (SPCC) Plan, if required
developed under guidelines set forth in 40 CFR, Section 112.3(a), (b).
■ Adequately train employees in the use of spill response equipment and
materials.
Inspection and Training
■ Perform and document in a log book frequent inspections of work
areas, waste storage facilities, maintenance areas, and contractor
projects to examine compliance with BMPs. Follow up with additional
training or enforcement as required. Incorporate inspection findings
into subsequent training efforts.
■ Design storm water pollution education programs to contain the
following elements:
- Promote the proper storage, use, and disposal of landscape
maintenance chemicals and other potentially harmful chemicals.
- Promote the use of safer alternative products such as: short-lived
pesticides, non -chlorinated solvents, water -based paints, non -
aerosol products.
- Encourage the use of "dry" washing processes for aircraft, vehicles,
and equipment.
TARGETED POLLUTANTS
< Oil and Grease
< Vehicle Fluids
< Fuel
< Solvents/Cleaning Solutions
< Battery Acid
< Pesticides/Herbicides/
Fertilizers
< Paint
< Metals _.
< Dumpster Wastes
< Sediment
• Landscape Waste
< Floatables
< Lavatory Chemicals and
Waste
< Runway Rubber Waste
< Other Miscellaneous
Chemicals
KEY APPROACHES
< Perform inspections and
enforcement
< Provide training for
employees
< Promote education of
vendors/public
< Show Storm Water Training
Video to employees
BMP10.doc BMP#10-1
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Inspection and Training (cont.)
■ Design storm water pollution education programs to contain the following elements:
- Encourage efficient and safe housekeeping practices in industrial activity areas.
- Increase awareness of the detrimental environmental impacts that result when fuel, antifreeze,
-pesticides, lubricants, detergents, paints and other wastes are dumped onto the ground or into
storm drains.
- Promote source reduction and recycling of waste materials.
- Increase awareness of possible penalties and fines associated with discharge of pollutants into
storm drains.
- Increase awareness of what is and what is not allowed to enter storm drains. Provide a
mechanism for violations to be reported.
REQUIREMENTS:
■ Capital and O&M costs are minimal for educational programs.
■ Educational programs need to be ongoing. Information and training must be disseminated at
regular intervals.
LIMITATIONS:
■ The success of educational programs is difficult to measure. Acceptance and awareness are
critical factors.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995-Multi-Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
I
BMP10.doc BMP#10-2
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_- _ _
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:hY
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PURPOSE:
TARGETED ACTIVITIES
Eliminate discharges to the storm drain system associated with ground
< Aircraft Lavatory
servicing of aircraft lavatory facilities. The sanitary sewage and associated
Service
rinse waters produced during the servicing of aircraft lavatory facilities must
< Lavatory Truck
be discharged to a wastewater treatment facility under appropriate
Cleanout/Backflush ing
permitting. Trucks or trailers equipped with bulk storage tanks are typically
used to service lavatory facilities. Non -storm water discharges and
residuals associated with servicing these facilities can be classified as
TARGETED POLLUTANTS
follows:
< Lavatory Chemicals
■ Discharges and residuals associated with diluting and mixing the
< Lavatory Waste
surfactants and disinfectants used for servicing lavatory facilities.
< Lavatory Truck Wash
■ Discharges and residuals associated with transferring materials from
Water
the aircraft.
■ Discharges and residuals associated with transporting and disposing
KEY APPROACHES
materials to the sanitary sewer system.
< Do not discharge
lavatory waste to
APPROACH TO FUTURE FACILITIES AND UPGRADES:
sanitary sewer
Design of New Facilities and Existing Facility Upgrades
connections other than
■ If possible, design triturator facilities to be covered, with low roll-over
triturator facilities
type berming.
< Utilize buckets or pans
■ Include a source of water at the triturator for clean up of lavatory service
to capture drippage
equipment.
from aircraft lavatory
■ Coordinate permitting of the triturator sanitary sewer connection through
access fittings
the local storm water and sanitary sewering agencies.
< Do not perform lavatory
■ Triturator facilities should not be located near storm drains.
truck cleanout or
backflushing at any
location other than
APPROACH TO EXISTING FACILITY ACTIVITIES:
triturator facilities
Operational Considerations
< Carry_ absorbent and
■ Do not discharge lavatory waste to sanitary sewer connections other
other containment
than triturator facilities. Other industrial -type connections may be
equipment on the
equipped with bypass gates which, if improperly maintained or
lavatory service
defective, may discharge to the storm water collection system.
equipment
■ Drain the aircraft connecting hose as completely as possible into the
storage tank after servicing an aircraft. Properly secure all hoses,
valves, and equipment when transporting waste to eliminate leakage
and spills.
■ Use only surfactants and disinfectants approved for discharge to the
sanitary sewer system. Do not discharge or rinse other unapproved
chemicals or materials into the triturator facility. Any change in the
chemicals used in aircraft lavatory service operations must be approved
by the Aviation Department.
BMP11.doc BMP#11-1
.CH_AR_ LOTTE%D:OUGLAS::I_NTERNATIONAL;AI_RPORT h.:`
1 min. I: L',i FG .��tY _-t:•- •�Cr;': ��. '�' �;t.-.,. :.
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BMP#11; 7. ,1: _ '_, °°°: r: L_ AVATOR_ Y:SERV_ICE_OPERA`TIONS
Operational Considerations (contd)
■ If possible, perform surf actant/disinfectant mixing and transfers in the triturator area or under cover.
This will allow the rinsing of minor spills and splashes to enter the sanitary sewer system.
■ Do not perform lavatory truck cleanout/backflushing at any location other than triturator facilities.
■ Utilize buckets or pans to capture drippage from aircraft lavatory access fittings. Immediately dump
the drippage into the bulk storage tank on the service cart or truck.
■ Carefully handle chemicals and chemical concentrates. Immediately collect dry chemicals or
absorb liquid chemicals for proper disposal. Do not hose down spills unless the discharge enters
the sanitary sewer system through a permitted connection (triturator facility).
■ Practice good housekeeping techniques at the triturator facility. Immediately clean spills of wastes
and chemicals.
Contingency Response
■ Carry absorbent and other containment equipment on the lavatory service equipment.
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
Inspection and Training
■ Perform regular inspections of the hose and fittings used for transferring lavatory waste. Keep the
equipment in good working order. Replace worn equipment before leaks develop. Notify
appropriate ground service personnel if it is noticed that the aircraft lavatory fittings require
maintenance.
■ Provide the appropriate level of employee training in the following areas: spill response and
prevention, storm water pollution prevention education (see BMP#10 for storm water pollution
education approaches), right -to -know awareness training, and hazardous materials management.
REQUIREMENTS:
■ Management practices are based on careful material handling, good housekeeping, and awareness
of maintenance requirements.
LIMITATIONS:
■ Facilities may have a limited number of permitted sanitary sewer access points (triturator facilities)
for a large quantity of lavatory service equipment.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995-Multi-Sector Storm Water General Permit
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
BMP11.doc BMP#11-2
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'. CH'ARLO-
TTWQ0V L $INTERNATIONAL AIRPORT : �.E.:76: ,¢•t
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BMP#12:
.� ,�- OUTDO.ORXAWAS_HDOWN%SWE_ E_PIN_G��:'�:
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+ "�'-."r-.5 ,�,;.. -'�, -
PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water from indoor
< Apron Washing
and outdoor washdown and sweeping operations.
< Ramp Scrubbing
< Outdoor/Power Washing
APPROACH TO FUTURE FACILITIES AND UPGRADES:
< Floor Washdown
Design of New Facilities and Existing Facility Upgrades
■
Consider contracting apron washing/sweeping services. Using
TARGETED POLLUTANTS
appropriate contractors will decrease waste handling responsibilities.
< oil and Grease
Inform contractors of their responsibilities regarding proper disposal of
< Solvents/Cleaning Solutions
sweeper and scrubber waste. Supply contractors with pertinent BMPs
Fuel
and operating specifications. Follow up with contractor inspections
<
< Aircraft Fire Fighting Foam
frequently.
(AFFF)
■
Incorporate appropriate waste receiving facilities for sweepers and
< Deicing/Anti-Icing Fluids
washing equipment. Coordinate sanitary sewer connection permitting
< Sediment
through the local sanitary sewering agency. '
< Floatables
■
Incorporate oil/water separators or other water quality devices into
project designs.
KEY APPROACHES
■
Consider incorporating gate valves in areas where apron washing will
< Collect and discharge wash
occur. The gate valves will direct wash water to the sanitary sewer in
water to the sewer
dry weather and will direct storm water to the storm drain system
< Use "dry" sweeping
during wet weather. Mechanical devices should be incorporated to
techniques
ensure that valves are not left open (to sanitary sewer) during wet
< Dispose of sweepings
weather. Coordinate permitting and connections through the local
sanitary sewering agency.
■
Employ berms to minimize run-on to other areas.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
■ Collect and discharge wash water to the sanitary sewer system
through a permitted connection.
■ Use designated and approved discharge facilities to dispose of waste
derived from apron/ramp cleaning.
■ Use "dry" sweeping techniques where feasible.
■ Dispose of sweepings in an appropriate manner.
■ Conduct berm repair and patching.
■ Inspect, clean, and maintain sumps and oil/water separators.
BMP12.doc
BMP#12- 1
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GHARLO.TTE/DOUGLAS.lNTERNATIONAL AIRPORT ';r j�`
2.'
BMP#1;.2
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-
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u
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Contingency Response
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
Inspection and Training
■ Provide the appropriate level of employee training in the following areas: spill response and
prevention, storm water pollution prevention education (see SC-10 for storm water pollution
education approaches), right -to -know awareness training, and hazardous materials management.
■ Develop regular maintenance and inspection programs for oil/water separators. Document
inspections and maintenance in a log book.
■ Characterize wastes derived from oil/water separators. Dispose of these wastes properly and
provide appropriate employee training.
REQUIREMENTS:
■ Capital costs vary depending on measures implemented.
- LOW COST: $50041,000 for berm construction.
- MEDIUM COST: $5,000-$20,000 for plumbing modifications (including re-routing discharge to
the sanitary sewer and installing a simple sump).
■ O&M costs increase with increasing capital investment.
LIMITATIONS:
■ Some wastewater agencies may require pretreatment and monitoring of wash water discharges
derived from apron washing to the sanitary sewer.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 122-124 NPDES Regulations for Storm water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
BMP12.doc
BMP#12- 2
-` . f. •a^ CHARLOTTE%D_ O.U_GLAS INTERNATI NA fi `-
B_ MP#13 - FI'R_E FIGHTING FOAM -DISCHARGE=,£
,�.%: "'..;� '_. ya. $i•'iv ., :�4,�g'~ .n,.,�:�^`_:s .,s •g'��! t±eti."'^,"a �'. F.- *, ,, �. ,a• �.
od•_i - - YnaS' ..'Y�F.iM...r g� `A. .� "ti¢�-"�b �. t,9• �,?etp _� �'a� v F, - .4,a .:�
PURPOSE: TARGETED ACTIVITIES
Eliminate discharges to the storm drain system associated with flushing or < Fire Fighting Equipment
testing of fire fighting foam (AFFF) systems. Testing and Flushing
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Design testing facility with the following characteristics:
- Located away from storm drain inlets, drainage facilities or water
bodies.
- Paved with concrete or asphalt, or stabilized with an aggregate base.
- Bermed to contain foam and to prevent run-on.
- Configure discharge area with a sump to allow collection and
disposal of foam.
■ Discharge foam waste to a sanitary sewer (industrial wastewater
permitting may be required). Foam waste shall not be discharged to
storm drains or water bodies.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
■ Perform fire fighting foam testing operations only in areas designated
by COP Aviation Department as appropriate for such activities.
■ Properly dispose of, or recycle, foam discharge.
■ Conduct berm repair and patching.
■ Regularly inspect, clean, and maintain AFFF collection sumps.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials,
in accessible locations near area of activity.
Inspection and Training
■ Regularly inspect testing facility.
■ Provide the appropriate level of employee training in the following
areas: spill response and prevention, storm water pollution prevention
education (see SC-10 for storm water pollution education approaches),
right -to -know awareness training, and hazardous materials
management.
TARGETED POLLUTANTS
< Aircraft Fire Fighting Foam
(AFFF)
KEY APPROACHES
< Perform testing operations in
designated areas
< Properly dispose of, or
recycle, foam discharge
< Service sump regularly
BMPI3.DOC BMP#13-1
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y.,.t. _
.CHARLOTTE%DOUGLASINTERNATIONAL AIRPORT;
- 4:i�"'�'T,':-�jy v`�1 iJ 'fir>'• - - �Y - - c _ _ -
a'
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_BMP_#i13 a FIRE FIGHTING': FOAM DIJ HAR E :' <. , . '-
i.wa- �� -;.d"'^ % :• �a, .. -^as r.a � � r t.g;�F,�::o s.<.w,� ��.ti� , � •may
',' y.. 'y' f�'�sl a�:�Y t;"!':�- fit. ,s._. ' - a - 3' �x, '•1. ...M-y, �' - _ � .3'
REQUIREMENTS:
■ Capital costs vary depending on measures implemented.
- LOW COST: $50041,000 for berm construction.
- MEDIUM COST: $5,000-$20,000 for plumbing modifications (including re-routing discharge to
the sanitary sewer and installing a simple sump).
■ O&M costs increase with increasing capital investment.
LIMITATIONS:
■ Some wastewater agencies may require permitting, pretreatment, and/or monitoring of this type of
discharge to the sanitary sewer.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
BMPI3.DOC BMP#13-2
-,CHARLOTTE/D_OUGL'AStlNTERNATIONAL AIRPORTY'�-` =
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-. "y"_ s• : ,a.r'i," si... ',y.d.�r., •.'^.'4o`=�f '_^� --_- _ -_ ?=::f.-;.-��•:�rc _ =r^�i� _ i� v; '.f''�;'i�,.,�"'r��`.,•c' �: -- `= �5*,'.:x,� -� * _ _ �8. 4'.7;,k�t...-� P'iL�..rr- U' ,:t":>. _•Si,cI�N."iPa` 'G_.a4 SYSTEMFBVP#1PWA�2.";..!irNsy. ir -�pa._ .�•'-S�tie�ui+
' . ¢•, `" :Fo-''.. Z. .3. _� ..•-: a -,: 4 -, �';�. -,aY. :2_°`; -:,3.: `' r.'
. -•1 8-_ - ti- ._ _ .. �'_� �-�-. .�',��[-�cl., it-: ... - �3.:._ ... '. - _ „ v .. _,__ --. - _rF� !.3 _a.h..^. i�.. :-cR. t2^. v... ..,
PURPOSE:
TARGETED ACTIVITIES
Eliminate discharges to the storm drain system associated with flushing of
< Aircraft potable water system
aircraft potable water systems.
cleaning and flushing
< Water truck cleaning and
APPROACH TO FUTURE FACILITIES AND UPGRADES:
flushing
Design of New Facilities and Existing Facility Upgrades
■ Design water truck flushing area with the following characteristics:
TARGETED POLLUTANTS
- Located away from storm drain inlets or drainage facilities.
- Paved with concrete or asphalt, or stabilized with an aggregate base.
< Purine
- Bermed to contain wastewater and to prevent run-on.
< Chlorine Bleach
- Configure discharge area with a sump to allow collection and
disposal of water.
■ Discharge water to a permitted sanitary sewer connection. Waste
KEY APPROACHES
water shall not be discharged to storm drains.
< Perform water truck flushing
in designated areas only
APPROACH TO EXISTING FACILITY ACTIVITIES:
< Collect all discharge from
aircraft potable water flushing
Operational Considerations
or water truck flushing and
■ Perform water truck flushing operations only in designated areas,
discharge to a permitted
designed with berms to prevent run-on and runoff. Do not perform
sanitary sewer connection
flushing near storm drains.
< Do not discharge water to the
ground or storm sewer
■ Collect all discharge from aircraft potable water flushing or water truck
connection
flushing containing Purine, chlorine bleach or other chemicals and
properly discharge to a permitted sanitary sewer connection, or recycle
the water.
■ Conduct berm repair and patching.
■ Inspect, clean, and maintain sumps and on -site treatment and
recycling units.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials
in accessible locations near area of activity.
Inspection and Training
■ Provide the appropriate level of employee training in the following
areas: spill response and prevention, storm water pollution prevention
education (see SC-10 for storm water pollution educational
approaches), right -to -know awareness training, and hazardous
materials management.
■ Monitor flushing operations regularly to ensure that proper collection
and disposal of discharge is being performed.
BMPI4.DOC BMP#14-1
A ir RNATIONAL, ,WPOUGL 9�"i
4�
j -x ZA*",
SYSTEM, FLUSH I NW P TULE
E$ ftt",ER'
REQUIREMENTS:
• Capital costs are low for implementation of collection system for aircraft potable water flushing.
• For new facility, capital costs vary depending on measures implemented.
- LOW COST: $500-$1,000 for berm construction.
- MEDIUM COST: $5,000-$20,000 for plumbing modifications (including re-routing discharge to
the sanitary sewer and installing a simple sump).
- HIGH COST: $30,0004150,000 for on -site treatment and recycling.
LIMITATIONS:
0 Some wastewater agencies may require pretreatment and monitoring of this type of discharge to
the sanitary sewer.
RELEVANT RULES AND REGULATIONS:
0 FR Vol. 60, No. 189, Sept. 25,1965 Multi -Sector Storm Water General Permit
0 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
0 40 CFR 401 Effluent Limitation Guidelines
BMP14.DOC BMP#14-2
'CH ARLO "'100 UGLAS INTERNATIONAL�AIRPORT
S• _ - `=:;; 2 w - .t--"::'?.: µ�:...,d �.e;.' _ -yc,.. . 4- :'� , h��,p - v.-t,�_,., >S :�c•
.. - r .�Sp s •> ` _ °'-r4: sf- .. .. -Z - :'� _ 3' ��i�i�
':v.b4r: ^�L �.'r�'�, {r.•' .sc re• .' .f-' a ..e 9� „G.. r," m'�'•r.
BMP#15 - . 'RUNWAY R, BBE R �� ,
:•<<r-Kx_rd;i,'vr,�°},;�'y" .-,?"•. _ a - ;A`ia •5, a -s.;T�;s.._:: r'.'%t�'',• s-'"'Y'''�' _`99::.t.
n}-: >.`-' �•�- ;rs'" . ,r. `8A l' _ _ _ - _ ii S' ch,T z.. - 2 +��- - �-^- r:' - ''�..
— '�' '��', - ' ".. -:a J �,.:�-: ';� LLt"rd• e . gyp• - -. �:..;.� :h s."• r . -. �.,
T`�'t'` . � ' tixs • �4,: a.. 'i. �ror'='. � •,. i � may' . �:i�a.' :r � -
PURPOSE: TARGETED ACTIVITIES
Eliminate discharges to the storm drain of particulate rubber generated by < Runway Rubber Removal
runway rubber removal activities.
APPROACH TO FUTURE FACILITIES AND UPGRADES:
Design of New Facilities and Existing Facility Upgrades
■ Design runway storm drain culverts to allow placement of particulate
capture devices, such as haybales or filter fabric, that will capture
rubber and dirt particles generated during runway rubber removal
activities.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations
■ Place devices that will capture rubber particulates, such as haybales or
filter fabric, over storm drain culverts or at other areas that will capture
rubber particulates generated during runway rubber removal activities.
■ Use manual or mechanical cleaning methods (ordinary mechanical
street sweepers) to remove rubber particulates from the runway and
adjacent paved areas after runway rubber removal activities.
Inspection and Training
■ Provide the appropriate level of employee training in the following
areas: spill response and prevention, storm water pollution prevention
education (see SC-10 for storm water pollution education approaches),
right -to -know awareness, and hazardous materials management.
■ Inspect storm drain culverts or runway drainage areas after runway
rubber removal activities.
REQUIREMENTS:
■ Capital and O&M costs should be low.
LIMITATIONS:
■ Runway drainage patterns may not be suitable for the collection of
rubber particulates.
RELEVANT RULES AND REGULATIONS:
FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General
Permit
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
TARGETED POLLUTANTS
< Rubber particles
< Dirt particles
KEY APPROACHES
< Use haybales or filter fabric
over culverts
< Use manual or mechanical
cleaning methods (e:g., street
sweepers) to remove
particulates following normal
removal process
BMPI5.DOC 13MP#15-1
s, CHA , TTE%DOU: ,L, I_NTERNATIONAL:AIRP,O,RT
r..
�..
'«4�` �•yy-r`4.. - �-�:5." �_� e 'r -., i-• ', ''�-,.. .�. • -_ .. ,'a' *rr',,,a,Y .^��,.
BIIIIP#16. �` >ti F -4o F �,��'�OIVINATER SEPARAT R"
O S
'`Y .t'' f - x�•.,, ""C ly��w?'���'�"���.; :r .,�
<_ •:.,. >��xr^'y- ,.F-':;;rl _,- _4 i; �',_ _ :j• .�s ;-? 7,':-a,c,.�"{ .`.�t"'F''y".rv'"-, ri, i
r?':s .:rdC;?fib. .'a1 .,�.-'t•.' e.r -'-,ie '; d,;°` >q;. .:�,,,�?�?.'. Y,%i-9�3�-^�',•rR�r'^>.£�;`��,,.e,'�ii,•�_:.< �i+''��:,'+-�' T�:
PURPOSE: TARGETED ACTIVITIES
Oil/water separators are baffled chambers designed to remove petroleum < Aircraft/Vehicle/
compounds and greases from storm water. Oil/water separators also remove Equipment Fueling
floatable debris and settled solids (sediment). < Aircraft/Vehicle/
Equipment Washing
APPROACH TO FUTURE FACILITIES AND UPGRADES: < Fuel/Chemical Storage
Design of New Facilities and Existing Facility Upgrades: < Installing, Cleaning, and
Oil/water separators are typically used in areas where the concentrations of Maintaining Oil/Water
petroleum hydrocarbons, floatables, or sediment may be abnormally high and Separators
source control techniques are not very effective. There are two types of
oil/water separators: the American Petroleum Institute (API) separator and TARGETED POLLUTANTS
the coalescing plate separator (CPS). Design, sizing, and placement of
oil/water separators is dependent on several factors including: tributary area, < Oil and Grease
type of activity, pollutant type and concentration, and water temperature. < Fuel
General sizing guidelines for API separators include the following: < Floatables
< Sediment
■ Horizontal velocity: 3 feet per minute.
■ Depth of 3 to 8 feet. KEY APPROACHES
■ Depth -to -width ratio of 0.3 to 0.5.
■ Width of 6 to 16 feet. < Frequently inspect and
■ Baffle height -to -depth ratios of 0.85 for top baffles and 0.15 for bottom clean separators
< Replace absorbent pads
baffles. as needed
CPS separator sizing is more complex. Sizing calculations require the
inclusion of information such as packing plate surface areas and plate
angles. CPS separators can, due to their packed plate design, remove the
same quantities of oils and greases while occupying less space than API
separators.
APPROACH TO EXISTING FACILITY ACTIVITIES:
Operational Considerations:
■ Separators must be inspected and cleaned frequently of accumulated oil,
grease, floating debris and sediments to be effective storm water quality
controls.
■ Oil absorbent pads are to be replaced as needed but will always be
replaced prior to the wet season.
BMP16.doc BMP#16-1
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a> .•a r c_
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Operational Considerations (continued):
■ The effluent shutoff valve will be closed during cleaning operations.
■ Any standing water removed during the cleaning operation must be disposed of in accordance with
federal, state, and local requirements.
■ Any standing water removed during the cleaning operation must be replaced with clean water to
prevent oil carry-over through the outlet.
Contingency Response
■ Maintain adequate supplies of spill response equipment and materials in accessible locations near
areas where spills may be likely to occur.
Inspection and Training
■ Provide the appropriate level of employee training in the following areas: spill response and
prevention, storm water pollution prevention education (see SC-10 for storm water pollution
education approaches), right -to -know awareness training, and hazardous materials management.
■ Perform and document in a log book all inspections and maintenance operations.
■ Develop a written operating, sampling, and reporting procedure under local storm water authority
guidelines. Train appropriate employees to implement these procedures.
REQUIREMENTS:
Capital and O&M Costs increase as the tributary area increases.
LIMITATIONS:
■ Oil/water separator installations should be designed and installed by experienced individuals. Little
data on the characteristics of petroleum hydrocarbons in storm water leads to considerable
uncertainty about separator performance.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plans)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
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T
_Z
EM ERG ENCY-SP I LL',CLEANUP__0.`;
NS.
4- A l,
PURPOSE:
TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water resulting from
< Aircraft/Vehicle/
petroleum products or other materials.
Equipment Deicing
< Aircraft/Vehicle/
GENERAL APPROACH:
Equipment Fueling
Owners and operators of facilities that store, process, or refine oil or oil
< Aircraft Lavatory Service
products may be required by federal law (40 CFR 112) to develop and
< Aircraft/Vehicle/
implement a Spill Prevention Control and Countermeasure (SPCC) Plan.
Equipment Washing
Emergency spill cleanup plans should include the following information:
< Cargo Handling
< Fuel/Chemical Storage
• A description of the facility including the owner's name and address,
< Pesticide/Herbicide Use
the nature of the facility activity, and at the general types and quantities
< Runway Deicing
of chemicals stored at the facility.
• A site plan showing the location of storage areas for chemicals, the
TARGETED POLLUTANTS
location of storm drains, site drainage patterns, fire water source
< Lavatory Chemicals and
locations, and the location and description of any devices used to
Waste
contain spills such as positive shut-off control valves.
< Fuel
• Notification procedures to be implemented in the event of a spill, such
< Oil and Grease
as key company personnel and local, state, and federal agencies.
< Solvents/Cleaning
• Instructions regarding cleanup procedures.
Solutions
< Pesticides/Herbicides/
• Designated personnel with overall spill response cleanup responsibility.
Fertilizers
< Battery Acid
APPROACH TO EXISTING FACILITY ACTIVITIES:
< Antifreeze
< Deicing Fluid
Operational Considerations
• Post a summary of the plan at appropriate site locations, identifying the
KEY APPROACHES
spill cleanup coordinators, location of cleanup equipment, and phone
numbers of regulatory agencies to be contacted in the event of a spill.
< Implement SPCC (if
• Maintain an inventory of appropriate cleanup materials on -site and
required)
strategically deploy cleanup materials based on the type and quantities
< SPCC implementation
of chemicals present.
training
< Immediate
• Make absorbent readily available in fueling areas.
containment/cleanup of
spills
Contingency Response
< Availability of spill
• Perform the following notifications in the event of a spill:
response equipment/
materials
- Fire Department
< Required agency
- Local Health Department
notification
- State Office of Emergency Services
- National Response Center - if spill exceeds reportable quantity (RQ)
• Containment and cleanup of spills shall begin immediately.
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'>-S' wir_' 7>-',y:.n y`:; ,?.-: .v,•. _+Ya, aec;b�' __ - ;s� L-.- _ ;a," :i
Inspection and Training
■ Provide formal training in plan execution to key personnel, with additional training for first responder
level personnel (29 CFR 1910.120). All employees should have basic knowledge of spill control
procedures.
REQUIREMENTS:
■ Capital and O&M costs should be small to moderate depending on the types and quantities of
� chemicals stored on -site.
■ Maintenance costs include periodic training and equipment replacement.
LIMITATIONS:
■ Spills occurring after work hours in confined areas may go undetected until impacting off -site areas.
RELEVANT RULES AND REGULATIONS:
• FR Vol. 60, No. 189, Sept. 25, 1995 Multi -Sector Storm Water General Permit
• 40 CFR 110.3 Discharge of Oil
• 40 CFR 112 Oil Pollution Prevention (SPCC/OPA Plan)
• 40 CFR 117.3 Determination of Reportable Quantities for a Hazardous Substance
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
BMP17.doc BMP#17-2
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rNa'
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PURPOSE: TARGETED ACTIVITIES
Prevent or reduce the discharge of pollutants to storm water from deicing and anti- Airfield Pavement Deicing
icing of airfield pavement. or Anti -icing
Operational Considerations
• Consider environmental characteristics of products when selecting SAE -
certified airfield pavement deicing products appropriate to climate and
operating conditions
• Physically remove snow and ice using plows and brooms prior to application of
chemical deicers to minimize the entrainment of deicers in plowed snow and
the volume of deicers required to achieve a safe pavement surface
• Employ application technologies and methods that minimize the volumes of
deicers required to achieve and maintain a safe pavement surface
Contingency Response
• Fill airfield deicing trucks in areas where spillage will be contained.
• Provide for containment of leakage from airfield -deicing trucks and deicer
storage facilities.
Inspection and Training
• Monitor pavement deicing operations regularly to ensure quantities of deicers
used are optimized for maintaining aircraft safety while minimizing excess
usage.
• Provide the appropriate level of employee training in the following areas:
implementation of methods and technologies to optimize pavement deicer
application, spill response and prevention, and storm water pollution
prevention education (see SC-10).
REQUIREMENTS:
• Airfield pavement deicing techniques must be consistent with the airport's
FAA -approved snow and ice control plan
LIMITATIONS:
• Only SAE -certified pavement deicers may be used on the airfield.
• Weather conditions limit the applicability of certain techniques for reducing
deicer usage.
RELEVANT RULES AND REGULATIONS:
• North Carolina General Statute 143-215.1
• 40 CFR 122-124 NPDES Regulations for Storm Water Discharges
• 40 CFR 401 Effluent Limitation Guidelines
TARGETED POLLUTANTS
• Urea
• Potassium acetate
KEY APPROACHES
• Physically remove snow
and ice to minimize
amounts of chemical
deicers required
• Apply only required
amounts of deicer to
maintain safe airfield
pavement conditions
• Properly handle airfield
pavement deicers
BMP18.doc BMP#18-1
Appendix F
Drawings
Figure I - Topographic Map of Outfall Locations
Figure 2 — Aerial Map of Drainage Areas and Outfalls
Figure 3 — Deicing Pads Location Map
Monitored Outfalls
• Other Outfalls ,� _ - _ { ^ „�-�^y/+ - 1 •a r
Drainage Basins t
1 • Ir'
,l
- .lrftal3,.-
A 0utfall ` Y , { • Outfall f
No DO
-� B Outfall �•
1 � tiv O
C Outlall
odd Rd
tt lANG
' 1 'D 1 0 - '•' Outfall
F Outfall
Taggart
C
�, 2 H1�, �w ii• reek
AN[J.
OangaLake .tr: -' �� ,�• T•Hangar �.
0 tfall - mj � -- _ OuHalI a
KOutlall Outfall
3 C No.000 'i
KWeat. I \ y t '�dr�../• �. �� •p t:
I .-. ` • 4 Air Cargo
1 ; Outwi
s. /'_`-" '•.�":%. 11 :..r. Santry •
. �! ,1 \ • - PostOutfall
}
i
a Q Outfall t r
Wesl B�y, OWall
a Outfall
�! �+ R Outlall No. 002 +r I 1
5.
� 1, it .�. `- � t- K ��` .f'• I ,
,�C `tfr T 1 {
01.E r
SCALE DESIGNED BY DATE DRAWING TITLE
AS SHOWN Figure 1. Topographic Mop of Outfoll
~ CDNFI➢EWIAL-ALL RIGHTS RESERVER-PFOUTI Or AVN BY DATE Locations
0 2000 BGS 31DEC14 Charlotte Douglas Airport
CHECKED BY DATE Charlotte, North Carolina
APPROX. SCALE, ft. JM 31DEC14 PROJECT rat AWIN Ha I REV.
ARRRDVED BY DATE 34y 4149Y FIGURE-1 0
CU. NORTH CARDuNA 21210 JM 31 DEC 1
Appendix G
Stormwater Pollution Prevention Plan Certification
L_ TIO =P 'VE�1 I :p .=
3. TpNI-N►'EI2�.P..;LU.I. R O1�TA.
—ATION'. M I,
-���V�IaO�ME�1 .AND °IMP � E �
North Carolina Division of Energy, Mineral, and Land Resources — Stormwater Permitting
Facility Name:
Permit Number:
Location Address:
County:
1A etk(� n 1
"I certify, under penalty of law, that the Stormwater Pollution Prevention Plan (SPPP) document and all attachments were
developed and implemented under my direction or supervision in accordance with a system designed to assure that qualified
personnel properly gather and evaluate the information required by the SPPP. Based on my inquiry of the person or persons
who manage the system, or those persons directly responsible for gathering the information, the information gathered is, to the
best of my knowledge and belief, true, accurate and complete."
And
"I certify that the SPPP has been developed, signed and retained at the narned facility location, and the SPPP has been fully
Implemented at this facility location in accordance with the terms and conditions of the sormwater discharge permit."
And
"I am aware that there are significant penalties for falsifying Information, including the possibility of fines and imprisonment for
knowing violations."
ISign (according to permit signatory requirements) and return this Certification. DO NOT I
SEND STORMWATER POLLUTION PREVENTION PLAN WITH THIS CERTIFICATION.
Signature
Print or type name of person signing above
Date
`, 12A
Title
SPPP Certification 10/13
����
NCDENR
North Carolina Department of Environment and Natural Resources
Pat McCrory
Governor
Brent Cagle
Charlotte Douglas International Airport
PO Box 19066
Charlotte, NC 28219
Dear Mr. Cagle:
Donald van der Vaart
Secretary
January 06, 2015
Subject: Acknowledgement of Permit Renewal
Permit NCO083887
Mecklenburg County
The NPDES Unit received your permit renewal application on January 02, 2015. A member of the
NPDES Unit will review your application. They will contact you if additional information is required to
complete your permit renewal. You should expect to receive a draft permit approximately 30-45 days
before your existing permit expires.
If you have any additional questions concerning renewal of the subject permit, please contact Julie
Grzyb (919) 807-6383.
Sincerely,
Inl re c , -rkt (for&
Wren Thedford
Wastewater Branch
cc: Central Files
Mooresville Regional Office
NPDES Unit
1617 Mail Service Center, Raleigh, North Carolina 27699-1617
Location: 512 N. Salisbury St. Raleigh, North Carolina 27604
Phone: 919-807-63001 Fax: 919-807-6492(Customer Service:1-877-623-6748
Internet:: www.ncwater.orq
An Equal Opportunit Mrmative Action Employer