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ADDITIONAL STORMWATER POLLUTION PREVEN110N MEASURES
VEHICLE AND EQUIPMENT MAINTENANCE
Descriotion and Puroose
Prevent or reduce the conlaminotlon of stormwater resulting from
vehlcle and equipment maintenance by running a"dry and clean site".
The besi optlon would be to perform maintenonce activities at an
offsite facility. If thls option is not available then work should be
per(ormed in designated areas only, while providing cover for materials
stored outside, checking tor leaks and spills, and contoining ond
cleaning up spills immediately.
Suitable Aoolications
These procedures are suitable on oll construction projects where an
onsite yard area is necessary for storage and maintenance of heary
equipment and vehicles.
Limilations
Onsite vehicle and equipment maintenance should only be used where it
is impractical to send vehlcles and equipment offsite for maintenance
antl repair. Sentling vehides/equlpment offsite should be done in
conjunction wilh a Slabilired Construction Entrance/Exit. Ouldoor vehide
or equipment maintenance is a potentially significant source of
stormwater pollution. Activities that can contaminate stormwater include
engine repair and service, changing or replacement of fluids, and
outdoor equipment storage and parking (engine fluid leaks�.
Imolementation
If maintenance must occur onsite, use designated areas, located away
from drainage courses. Dedlwted maintenance areas should be
proteded irom stormwater runon and runo(f, and should be bcated at
least 50 ft from downstream drainage facilities and watercwrses.
Drip pans or absorbent pads should be used during vehicle and
equipment maintenance work that imolves fluids, unless the
maintenance work is performed over an Impermeable surface in a
dedicated maintenance area.
Ploce a stock ile of s ill deanu moterials where it will be readil
P P P Y
accessible.
AIl fueling irucks antl fueling oreas are required to hove spill kits
and/or use other spill protection devices.
Use adsorbent materials on small spills. Remove the absorbent
materials prompUy and dispose o( properly.
Insped onsite vehicles and equlpmenl daily at siartup (or leaks, and
repair Immediotely.
Keep vehides and equipment dean; do not allow excessive build—up of
oil and grease.
Segregate and recycle wastes, such as greases, used oil or oil filters,
antifreeze, deaning solutions, automofive batteries, hydraulic ond
transmission fluids. Provide secondary containment and covers (or these
materials if stored onsite.
Troin employees and subcontroctors in proper mointenonce and spill
cleanup procedures.
Drip pans or plastic sheeting should be placed under all vehicles and
equipment placed on docks, barges, or other structures over water
bodies when the vehide or equipment is planned to be idle for mare
than 1 h0uf.
Properly dlspose of used oils, fluids, lubricants, and spill deanup
moterials.
Do not place used oil in a dumpster or pour into a storm drain or
watercourse.
Properly dispose of or recyde used batleries.
Do noi bury used tires.
Repair leaks of Ouids and oil immediately.
Listed below is further information if you must perform vehide or
equipment maintenance onsite.
InsoecCion and Maintenance
Inspect and verify lhat BMPs are in place prior to the commencement
of associated activities. While activities associated with the BMP are
under way, Inspect weekly to verify continued BMP implementation.
Keep ample supplies of spill deanup moteriols onsite.
Mainlain waste fluld containers in leak proof condifion.
Vehides and equlpmenl should be Inspected on each day of use. Leaks
should be repaired immediotely or the problem vehicle(s) or equipment
should be removed from the project site.
Inspect equipment for damaged hoses and leaky gaskets routinely.
Repair or replace as needed.
RELEA5E0 FOR CONSTRIICTI�N
Su6jec��o compliance with allregula�ions
of S�a�e antl Local Codes
City of Carmel
r
�un��\i lo•rvalM.��
DATE: 06�� 7�20
VEHICLE AN� EQUIPMENT FUELING
Descriotion and Pumose
Vehlcle equipment fueling procedures and practices are designed to
prevent fuel spills and leaks, and reduce or eliminate contaminailon of
stormwatec This can be accomplished by using o(fsite facilities, fueling
in designated areas only, endosing or covering stored fuel, implementing
spill controls, and training employees and subconhactors in proper
fueling procedures.
Limitations
Onsite vehlcle and equipmenl fueling should only be used where It is
impractical to send vehides and equipment offsite for fueling. Sending
vehicles and equipment offsile should be done in conjunction with a
Stabillzed Construction Enirance� Exit.
Imolementation
Use offsite fueling stations as much as possible. These businesses are
better equipped to handle fuel and spills properly. Performing this work
offsite can also be economical by eliminaEing the need for a separate
(ueling area at a site.
Discourage °topping—off' of fuel tanks.
Absorbent spill deanup materials and spill kits should be available in
fueling areas and on fueling trucks, and should be disposed of properly
after use.
Drip pans or absorbent pads should be used during vehide and
equipment fueling, unless the fuefmg Is performed over an impermeable
sur(ace in a dedicated fueling area.
Use absorbent materials on small spills. Do not hose tlown or bury the
spill. Remove the adsorbent materiols promptly ond dispose of propedy.
Avoid mobile (ueling of mobile construction equipment around the site;
rather, transport the equipment to designated fueling areas.
Train em lo ees and subcontractors in ro er fuelin and deanu
P Y P P 9 P
procedures.
Dedicated fueling areas should be protected from stormwater runon and
runoff, and should be localed at least 50 fl away from tlownstream
drainage facilities and walercourses. Fueling must be performed on
level—grade areas.
Protect fueling areas with berms and dikes to prevent runoq runoff,
and lo contain spills.
Nozzles used in vehide and equipment fueling should be eqdipped with
an automatic shutoif to control drips. Fueling operatians should not be
left unattended.
Federal, state, and local requlrements should be observed for any
stationary above ground storage lanks.
Insoection and Maintenance
Vehlcles antl equipment should be inspected each day of use for leaks.
Leaks should be repoired immediately or problem vehicles or equipment
should be removed (rom the project site.
Keep ample supplies of spill cleanup materials onsite.
Immediately clean up spills and properly dispose of contaminated soil
and cleanup materials.
SOLID WASTE MANAGEMENT
Description and Puroose
Solid waste management procedures and practices are designed to
prevent or reduce the dlscharge of pollutants to stormwater from solld
or construclion wasle by providing designated waste collection areas
and containers, arranging for regular disposal, and training employees
and subcontraciors.
Sultable Apolications
This BMP is suitable for construction sites where the following wastes
are qeneratetl or stored:
Solid waste generated from trees and shrubs removed during land
dearing, demolition of existing structures (rubble), and building
construction
Packaging materials including wood, paper, and plastic
Scrap or surplus building materials induding scrap melals, rubber,
plastic, glass pieces and masonry products
Domestic wastes including food conlainers such as beverage cans,
coffee cups, paper bags, plostic wrappers, and cigorettes
Consiruction wastes 'mduding brick, mortar, timber, steel and metal
scraps, pipe and electrical wttings, nonhamrdous equipment parts,
styrofoam and other materials send transport and package construction
materials
Imolementafion
The following steps will help keep a clean sile and reduce stormwater pollution:
Select designated waste colleclion areas onsite.
Inform trash—hauling contractors that you will accept only watertight dumpsters for onsite use.
Inspect dumpsters for leaks and repair any dumpster that is not watertight.
Provide an adequate number of containers with lids or covers that can be placed over the container to
keep rain out or to prevent loss of wastes when it is wintly.
Plan for addiYional containers and more frequent pickup during the demolition phase of construction.
Collect site trash daily, especially during rainy and windy conditions.
Remove this solid waste prompUy since erosion and sediment control devices tend to collect litter.
Make sure that toxic liquid wastes (used oils, solvents, and paints) and chemicals (acids, pesticides,
additives, curing compounds) are not tlisposed of in dumpsters designated for constructlon debris,
Do not hose out dumpsters on the construction site. Leave dumpster deaning lo the trash hauling
contractor.
Arrange for regular wasie colleciion 6efore containers overFlow.
Clean up immediately if a container does spill.
Make sure that construction waste is collected, removed, and disposed of only at authorized disposal
areas.
CollecPion. Storage. and Disposal
Littering on the project site should be prohibiled.
To prevent dagging of the storm drainage system, lilter and debris removal from drainage grales,
trosh rocks, and ditch lines should be a priority.
Trash receptades shoultl be pravitled in the contractor's yard, fleld trailer areas, and at bcatlons
where workers congregate for lunch ond break periods.
Litter from work areas within the constructian limits of the project site should be collected and placed
In waterfight dumpsters at least weekly, regardless of whether the litter was generated by he
contractor, the public, or others. Collected litter and debris should not be placed in or next to drain
Inlets, stormwater drainage systems, or watercourses.
Dumpsters of sufficient size and number should be provided to mntain the solid waste generated by
the projecl.
Full dumpsters should be removed fram the project site and the conients should be disposed of by
the trash hauling cantractor.
ConsUuction debris and waste should be removed from lhe site blweekly or more frequently as needed.
Construction material visible to the public should be stored or stacked in an orderly manner.
Starmwater runon should be prevented from contacting stored solid waste thraugh the use of berms,
dikes, or other temporary diversion shuctures or through the use of ineasures to elevate waste from
site sur(aces.
Solid waste storage areas should be located at least 50 ft from drainage facilities and watercourses
and should not be located in areas prone to flooding ar ponding.
Insoecfion and Maintenance
Inspect and verify that activity—based BMPs are in place prior lo the commencemenl of associated
activities. While acPivities associated with the BMP are under way, Inspect weekly to verify continued
BMP implementation. A certified indlvidual approved by EHS lo conduct lhe weekly and after every z"
rain event storm water BMP inspections.
Inspect BMPs subject to non—stormwater discharge daily while non—stormwater discharges ocar
Inspect construclion waste area regularly.
Arrange for regular waste colleciion.
DE—WATERING AND PUMPING OPERATIONS
Descriplion and Purpose
De—watering opewtions are practices that manage the discharge of pollutants when
non—stormwater and accumulated precipitatian must be removed from a work bcation so that
constructlon work may be accomplishetl.
Suitable Applications
These practices are Implemenied for discharges of non—storm water from canstruction sites.
Non—stormwaters include, but are nol Ilmited lo, groundwater, water (rom cofferdams, water
diversions, and waters used during construction activities that must be removed from a work
area. Practices identified �m this section are also appropriate for implementation when managing
the removal of accumulated precipilalion(stormwater) from depressed areas at a constructlon
site.
Limitations
Sile conditions will dictate design and use of dewatering operatlons. The controls discussed in
this best management practice (BMP) address sediment only. The controls detailetl in this BMP
only allow for minlmal settling time for sediment parCicles. Use only when site conditions restrict
the use o( the other control methods. Dewatering operations will require, and must comply with,
applicable local permits.
Imolementation
De—walering discharges must not cause erosion at the discharge point A wriety of inethods
can be used to treat water during de—watering operations. Several devices are presented below
and provide oplions to achleve sediment removaL The size of particles present in the sediment
and Permit or receiving water limitations on setliment are key consideratlons for selecting
sediment treatmenl oplion(s); in some cases, lhe use o( multiple devices may be appropriate.
PUMP
ICHAR
HOSE
oallor°� � � �
DEWATERING
BA� FILTERED 15'x15' DANDY DEWATERING
WATER BAGS, CAPABLE OF FLOW RATES
TIE �OWN STRAP � � EQUAL TO OR GREATER THAN
95 GAL/MIN/SQ.R OR
PUMP DISCHARGE HOUSE� APPROVED EQUAL.
FILTERING PAD TO BE
25x25' M LOCATIONS AS
REQUIRED TO KEEP �
SEDIMEM FROM EMERING
WATERS OF THE US. DO IP�
NOT ALLOW DISCHARGE
TO FLOW DIRECTLY TO
— 50' MIN. VEGEfATED BUFFER
BEFORE DISCHARGE ENTERS
CREEK. IF NO BUFFER, INSTALL
TEMPORARY SEDIMENT BASIN.
WATERS OF U.S. � �COMPACTED SUBGRADE � ���
(1) 6" COURSE Dw 6" RIP RAP AT
#B WASHED STONE OUTLET. IN ADEQUATE
FILTERING PAD. QUANTITIES TO PREVENT
EROSION.
NOTE:
CONTRACTOR IS RESPONSIBLE FOR DETERMINING HOW MANY DEWATERING BAGS ARE REQUIRED, THE
LOCATION AND THE NUMBER AND 9ZE OF PUMPS REpURIRED. IF CONTRACTOR FEELS THAT THE
15x15 FILTERING PADS ARE INADEQUATE TO HOLD ENOUGH BAGS, HE SHALL DISCUSS ADDITIONAL
LOCATIONS AND SIZES WITH THE ON—SRE ENGWEER. WHEN DEWATERMG BAG IS FULL OF SEDIMENT,
REMOVE BAG AND DEPOSIT SEDIMENT IN A LOCATION DETERMMED BY THE ON—SITE ENGMEER.
GRAVITY BAG FILTER
Description:
A gravity bag filter, also referred to as a dewatering bag, is a square or rectangular bag made
of non—woven geotextile fabric that mllects sand, silt, and fines.
Appropriate Applications:
Effective for the removal of sedlments (gravel, sand, antl silt). Some metals are removetl with
the sediment.
Implementation:
Water is pumped into one sitle of the bag ond seeps through the bottom and sides of the bag.
A secondary barrier, such as a rock filter bed or straw/hay bale barrier, is placed beneath and
beyond the edges of the bog to capture sedlments that escape the bag.
Maintenance:
Inspection of lhe flow conditions, bag condition, bag capacity, and the secondary barrier is
required.
Replace the bag when it no longer filters sediment or passes water ai a reasonable rate. The
bag is disposed of offsite.
SEWN IN
SPOUT
— WATER
PUMP
TIE DOWN
STRAP
OANDY DEWATERING BAGTM
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DANDY DEWATERING BAG
DE-WATERINGNoPRAAEICES DETAIL �
C802
No. -
LA20700037
STATE OF
oarz�. 00%oosoo
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Schneider
(i�fOMATICS
a division of
The Schneider Corporation
Historic Fort Harrison
8901 Otis Avenue
Indianapolis, IN 46216-1037
Tel eph on e: 317826 J100
ww w. sch n eid ercorp. com
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STORMWATER POLLUTION
PREVENTION DETAILS
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