|
Compliance
Corner
In the United
States, hazardous wastes are subject to regulations mandated by
the Resource Conservation and Recovery Act (RCRA). Every month on
this page we provide clear, in-depth guidance on a different aspect
of the RCRA regulations. The information presented here is taken
from McCoy's RCRA Unraveled,
2010 Edition and is copyrighted by McCoy and Associates, Inc.
One thing you
will notice as you read the guidance presented below is references
to RCRA Online (RO) documents. These are letters, memos, or other
guidance documents issued by EPA and are often the source of the
information presented here. Each document is referred to with a
five-digit code (e.g., RO 11594). The most convenient way to obtain
copies of these documents is to use EPA's Internet-based document
retrieval service. This service, called RCRA
Online, is an excellent, free database developed by EPA. Go
to RCRA Online's Advanced Search Page. The second data-entry box
from the top on the right-hand side of the Advanced Search page
asks for the RCRA Online Number. Enter the five-digit RO code you
are interested in and click on the Search button. A "Search
Results" page will come up giving you a hyperlink and an abstract
of the document. Clicking on the hyperlink will retrieve the "Record
Detail" of the document, providing a summary and (finally)
a page icon hyperlink to the full text of the document.
Universal
Wastes
We have
discussed the universal waste program regulatory structure
and requirements for universal waste handlers in previous
editions of the Compliance Corner. In this installment,
we discuss three additional universal waste topics: 1) requirements
for universal waste transporters and destination facilities,
2) state authorization issues, and 3) the effects
of the Mercury-Containing and Rechargeable Battery Management
Act.
1.
Universal waste transporter and destination facility requirements
The
function of transporters and destination facilities in the
universal waste program is described in the next two sections,
respectively.
Transporters
A universal
waste transporter is a person/entity engaged in the offsite
transportation of universal waste by air, rail, highway,
or water. [§273.9] If a handler transports any amount
of universal waste, he/she is a transporter subject to Part
273, Subpart D; there is no de minimis cut-off amount like
there is for used oil generators who can transport up to
a certain amount and still remain just a generator. [RO
14088] Companies that are not hazardous waste transporters
can be universal waste transporters. This is true because
no manifests are required for universal waste shipmentsjust
bills of lading.
Like
universal waste handlers, transporters are prohibited from
treating, recycling, or disposing universal wastes. They
also must immediately contain any spills or releases of
materials and must manage any cleanup residue that fits
the definition of hazardous waste under full RCRA requirements.
Finally, they may only transport universal wastes to a universal
waste handler, a destination facility, or a foreign destination.
Transporters
may only store universal wastes at a transfer facility for
ten days or less. If they exceed this time limit, they become
universal waste handlers subject to the small or large quantity
handler requirements. [§273.53(b), RO 14186]
DOT
requirements
Universal
waste transporters are fully subject to DOT requirements,
spelled out in 49 CFR Parts 171180. Note, however,
that even though they are hazardous wastes under RCRA, universal
wastes are not hazardous wastes under DOT rules (because
shipments of these wastes dont require a manifest).
Thus, the word waste should not be used in front
of or in a shipping description. [§273.52(b)] Instead,
transporters of universal waste shipments must comply with
the DOT requirements that would be applicable if the waste
were being transported as a product. For example, in an
October 1, 1998 DOT letter (Ref. No. 98-0250), DOT noted
that Mercury contained in manufactured articles
may be used to describe shipments of universal waste fluorescent
light bulbs. Table 1 lists DOT shipping descriptions for
batteries that are commonly managed as universal waste.
When
transporting universal waste batteries:
[T]he
transporter must comply with the appropriate DOT requirements,
which are based on whether the particular battery type is
a DOT hazardous material, and if so, which DOT hazardous
material requirements apply to the specific battery type.
[May 11, 1995; 60 FR 25501]
On April
3, 2009, DOT wrote a public letter (available at http://www.phmsa.dot.gov/staticfiles/PHMSA/DownloadableFiles/Files/2009_Battery_Safety_Compliance_Advisory.pdf)
to battery recyclers and other battery handlers to emphasize
the need to properly package spent batteries before shipping
them offsite. In that letter, DOT noted an ongoing trend
of serious safety problems and noncompliance related to
the classification, packaging, marking, labeling, documentation,
and transportation of spent batteries. Common violations
and safety problems noted include:
-
Large
numbers of used batteries, of many different types, are
collected in large containers that do not adequately prevent
damage to the batteries or prevent their release during
transportation.
-
Outer
packages are not marked and labeled as required to indicate
that they contain batteries, and the shipments are not
described properly on the accompanying shipping documents.
-
No
action is being taken to prevent a short circuit, such
as separating the batteries by placing each one in a separate
plastic baggie or taping the terminals of
the battery.
The
April 3, 2009 letter contains a summary of the DOT requirements
that apply to ground shipments of batteries for recycling
or disposal. See also DOT Interpretation 09-0090, available
at http://phmsa.dot.gov/hazmat/regs/interps.
On January
14, 2009 [74 FR 2200], DOT issued a final rule that 1) clarifies
the requirement that batteries and battery-powered devices
be offered for transportation and transported in a manner
that prevents short circuiting, the potential of a dangerous
evolution of heat, and/or damage to terminals; and 2) includes
several examples of packaging methods that can be used to
meet this requirement. This may be achieved by packing each
battery in fully enclosed inner packagings made of nonconductive
material or separating the batteries from each other and
other conductive material (e.g., metal) in the same package.
Compliance with this new rule was required beginning January
1, 2010.
Q
What requirements apply to lithium batteries when
they are shipped offsite to a battery reclaimer?
A
A hazardous waste manifest is not needed for shipments
of universal waste. However, the DOT hazmat regulations
will continue to apply if the universal waste meets the
definition of a hazardous material or a hazardous substance.
Lithium batteries meet the definition of a hazardous material
(Class 9); thus, full compliance with the DOT regulations
will be required (e.g., shipping papers, markings, packaging
requirements).
For
ground shipments of lithium batteries (including lithium-ion
batteries), batteries have to be separated or packaged so
as to prevent short circuits and must be packed in a strong
outer packaging or contained in equipment. [Special Provisions
188 and 189 of 49 CFR 172.102 and 49 CFR 173.185(d)] For
example, the batteries could be individually packaged in
plastic baggies or have their terminals taped to prevent
short circuits.
Destination
facilities
According
to §273.9, a universal waste destination facility is
any entity that treats, recycles, or disposes a particular
category of universal wastes. Because these activities pose
significant risks to human health and the environment, destination
facilities are subject to the same management standards
as any other TSD facilities managing hazardous waste. First
and foremost, they must have a RCRA permit [unless they
are a §261.6(c) permit-exempt recycling facility].
Additionally, all equipment must be designed and operated
in accordance with the Part 264 or 265 management standards,
and the substantive and administrative land disposal restrictions
(LDR) program requirements are applicable, including recordkeeping.
[64 FR 36481] The destination facility is typically the
first facility handling universal waste that is responsible
for compliance with any LDR provisions. [RO 14088] However,
if the destination facility is a solid (nonhazardous) waste
landfill, the handler will have to ensure that any decharacterized
universal wastes or nonhazardous residues from treating
universal waste meet LDR treatment standards before they
go into that landfill. [RO 14756]
Destination
facilities are subject to requirements in Part 273, Subpart
E. In addition to the above major requirements, they are
required to maintain a record of all universal wastes they
receive via a log or by keeping copies of invoices, bills
of lading, or other shipping documents.
When
containers of universal waste are shipped from a handler,
they are labeled as universal wastesnot hazardous
wastes. When these wastes are received at destination facilities,
though, they are managed under the facilitys hazardous
waste permit. EPA has noted that such containers of universal
waste received at destination facilities do not have to
be relabeled as hazardous waste. [RO 14088]
2.
State authorization issues
The
universal waste program was not promulgated to implement
the HSWA amendments to RCRA. Therefore, the universal waste
program took effect on May 11, 1995 only in those states
that were not authorized for the base RCRA program. In authorized
states, the universal waste rules werent effective
until states revised their hazardous waste program to incorporate
the regulations. [60 FR 25536, RO 11952] Similarly, when
EPA added hazardous lamps to the program (effective January
6, 2000 at the federal level), that rule was not effective
in authorized states until they adopted it.
For
handlers and transporters, the universal waste program is
less stringent than preexisting RCRA hazardous waste
rules. Therefore, states are not obligated to add this program
to their existing regulatory structure (although EPA encourages
states to do so). Thus, the universal waste program has
taken effect only in those authorized states that have chosen
to adopt and administer either the federal universal waste
program or their own (no-less-stringent) version of the
program.
Current
state status
The
map in Figure 1 shows the current adoption status of the
base (May 1995) universal waste program in the United States.
All states have 1) become authorized to administer
this program, 2) adopted the universal waste program,
or 3) EPA administering the program (Alaska and Iowa).
Interstate
transport
States
may add other materials to their own universal waste program
(e.g., paint and paint-related wastes are universal wastes
in Texas). These situations present logistical problems
for the interstate transportation of these wastes.
When
shipping to another handler or a destination facility, a
universal waste handler must know whether the states that
his/her waste is being shipped to or through regulate the
specific wastes being shipped as universal waste. In those
states that do regulate the specific wastes in the shipment
as universal waste, compliance with only the Part 273 standards
will be required. In those states that do not regulate the
wastes as universal waste, compliance with the full hazardous
waste provisions is required, including the use of manifests
and hazardous waste transporters. [June 12, 2002; 67 FR
40520] There have been instances where a truck has broken
down in a state that has not adopted the waste as universal
waste, and the handler/transporter was fined for having
unmanifested hazardous waste onboard.
In some
cases, a waste regulated as universal waste in one state
may be sent to a state where it is still subject to the
full set of hazardous waste regulations. For the part of
the trip through the originating state and any other states
where the waste is regulated as universal waste, neither
a hazardous waste transporter nor manifest would be required.
However, when the waste travels through the receiving state
and any other states that still consider the waste to be
hazardous, a manifest is required and transport must be
accomplished by a hazardous waste transporter. In these
situations, the originating facility should complete a manifest
and send it to the transporter who will be carrying the
waste through the first state that considers the waste to
be hazardous. EPA recommends that the originating facility
note in Block 14 of the manifest that the waste is covered
under the universal waste regulations in the originating
state, but not in the receiving facilitys state. The
receiving facility would then sign the manifest and send
it back to the originating facility. [May 11, 1995; 60 FR
25537] Although EPAs guidance is silent on the matter,
an LDR form would also be required by the receiving facility;
thus, it would be necessary for the originating facility
to also forward an LDR form to the receiving facility (e.g.,
sending it to the transporter who will be carrying the waste
through the first state that considers the waste to be hazardous).
Hazardous
waste that is not regulated as universal waste in the originating
state may sometimes be sent to a state where it qualifies
as universal waste. In this case, the waste must be carried
by a hazardous waste transporter in the originating state
and any other states where it is not a universal waste.
The originating facility would need to complete a manifest
and give copies to the transporter who picks up the waste.
However, transportation in the receiving state and any other
states where the waste is universal waste would not require
a manifest or need to be carried out by a hazardous waste
transporter. Even so, the originating facility is responsible
for ensuring that the manifest is forwarded to the receiving
facility and for obtaining a signed copy back from the receiving
facility. Again, EPA recommends that the originating facility
note in Block 14 of the manifest that the waste is covered
under universal waste regulations in the receiving state,
but not in the originating state. [May 11, 1995; 60 FR 25537,
RO 14088] Although the receiving facility may not require
an LDR form from the generator in this situation, the generators
state RCRA program will require that the generator complete
the appropriate LDR form per the state equivalent of §268.7(a).
Additionally, even though EPAs guidance suggests that
LDR forms are not required for shipments of universal waste,
some receiving facilities may require them anyway if they
will be treating or recycling the waste.
3.
Mercury-Containing and Rechargeable Battery Management Act
In May
of 1996, the Mercury-Containing and Rechargeable Battery
Management Act became law. This law was designed, among
other things, to 1) standardize efforts already underway
in over a dozen states to promote the recycling or proper
disposal of lead, mercury, nickel-cadmium, and other types
of rechargeable batteries; and 2) limit the mercury
content of consumer batteries. In a nutshell, the act:
-
Requires
all 50 states to implement collection, storage, and transportation
provisions that are identical to the universal waste program
requirements promulgated on May 11, 1995 for 1) rechargeable
nickel-cadmium batteries, 2) lead-acid batteries
not covered by Part 266, Subpart G, 3) rechargeable
alkaline batteries, 4) certain mercury-containing
batteries banned from domestic sale, and 5) used
consumer products containing rechargeable batteries that
are not easily removable [RO 14020, 14088, 14290];
-
Limits
the mercury content of alkaline-manganese button-type
batteries;
-
Prohibits
the sale of nonbutton-type alkaline-manganese batteries
and all zinc-carbon batteries that contain intentionally
added mercury;
-
Prohibits
the sale of button-type mercuric-oxide batteries and other
types of mercuric-oxide batteries, except where nonbutton
battery manufacturers or importers have identified an
approved recycling collection site and informed battery
purchasers of this site;
-
Mandates
that rechargeable nickel-cadmium and certain small sealed
lead-acid (SSLA) batteries in consumer devices be easily
removable; and
-
Establishes
national, uniform labeling requirements for rechargeable
and other regulated batteries and associated packaging.
On September
22, 1998 [63 FR 50569], EPA approved a new label for rechargeable
batteries that helps consumers identify recyclable batteries
and locate the nearest battery collection center. [RO 14483]
EPA
has noted that the §§273.13(a)(2)/273.33(a)(2)
provision that allows handlers to remove electrolyte from
certain batteries is covered under the auspices of the battery
act. This means that states may not alter this provision
when implementing their own version of the universal waste
program. [RO 14124]
States
that have battery management standards are required by the
law to have programs identical to the federal universal
waste program for the management of these materials. Hazardous
waste batteries that meet the definitions in the law must
be managed as universal waste. [EPA/530/K-05/019] Although
the law clearly requires all states to have a national,
uniform set of collection, storage, and transportation regulations
(identical to the universal waste program) for the noted
types of batteries, the law does not address the subsequent
recycling or disposal of those batteries. Thus, states may
adopt battery recycling or disposal standards that are more
stringent than existing federal requirements under RCRA.
A good
summary of this law is available in Implementation of
the Mercury-Containing and Rechargeable Battery Management
Act, EPA/530/K-97/009, November 1997, available from
http://www.epa.gov/epawaste/hazard/recycling/battery.pdf.
Disclaimer
Considerable
care has been exercised in preparing this document; however, McCoy
and Associates, Inc. makes no representation, warranty, or guarantee
in connection with the publication of this information. McCoy and
Associates, Inc. expressly disclaims any liability or responsibility
for loss or damage resulting from its use or for the violation of
any federal, state, or municipal law or regulation with which this
information may conflict. McCoy and Associates, Inc. does not undertake
any duty to ensure the continued accuracy of this information.
This document
addresses problems of a general nature related to the federal RCRA
regulations. Persons evaluating specific circumstances dealing with
the RCRA regulations should review state and local laws and regulations,
which may be more stringent than federal requirements. In addition,
the assistance of a qualified professional should be enlisted to
address any site-specific circumstances.
|