Common
RCRA Violations
Although
we havent found any nationwide statistics on the most
common RCRA violations, the state of Colorado provided us
with a summary of its findings. Table 1 identifies
the most common RCRA violations in Colorado, for both large
and small quantity generators of hazardous waste, from 1997
through 2006. We believe that these lists are representative
of what happens in other states as well. Each RCRA violation
is discussed in more detail in the subsections that follow.
Training
violations
We believe
facilities typically receive NOVs for either 1) not
providing adequate training to their personnel, or 2) more
commonly, not having documentation showing that their people
received training (even if they actually did). The RCRA
training requirements are codified in §264.16 (for
permitted TSD facilities), §265.16 (for interim status
TSD facilities and large quantity generators), and §262.34(d)(5)(iii)
(for small quantity generators).
The
regulations are not very specific with respect to training
program content. However, they are very specific with respect
to the training records that must be maintained at a facility.
Therefore, most RCRA training violations stem from failure
to comply with the recordkeeping requirements, rather than
the content of the training program itself.
We get
a call about once a month from a customer who is expecting
a state or EPA inspection and cant find the certificate
of attendance that he or she received at one of our RCRA
training seminars. These people know that, no matter what
else may be inspected, training records are a for-sure
item (so we fax them a copy).
To minimize
compliance problems associated with training, establish
a bulletproof training records retention program to meet
the requirements of §§264/265.16(de). This
will go a long way towards eliminating the number one source
of NOVs for noncompliance with the RCRA regs.
Another
common trigger for NOVs related to training is when an EPA
or state inspector observes noncompliance with some other
aspect of the RCRA regs. In this case, they will often check
to see if the responsible personnel were trained in that
area. For example, if hazardous waste containers are left
open or are not properly labeled, in addition to issuing
an NOV for those violations, inspectors may also want to
review the training program for facility personnel responsible
for those activities. If the training program does not adequately
address container management and labeling, this could be
the basis for another NOV. To help prevent such enforcement
issues, review the top ten RCRA violations for your generator
class in Table 1, and make sure these activities are
covered adequately in the training programs for the appropriate
personnel.
Contingency
plan violations
The
requirement for large quantity generators to have a contingency
plan is in §262.34(a)(4), which references compliance
with Part 265, Subpart D. Small quantity generators are
subject to the less-stringent provisions in §262.34(d)(5),
which are discussed below. TSD facilities are also required
to have contingency plans. [See Part 264/265, Subpart D.]
One of the most common reasons for NOVs associated with
contingency plans at large quantity generator and TSD facilities
is that the emergency coordinators information (names,
phone numbers, addresses, etc.) in the contingency plan
is out of date. [§§264/265.54(d)] Keeping this
information up to date is a challenge, because it changes
rapidly, but its important and something inspectors
check carefully. Incomplete contingency plans also regularly
result in NOVs.
Another
difficulty with contingency plans is that they must be reviewed/coordinated
with local authorities (police, fire departments, hospitals,
and emergency response teams) and sometimes this doesnt
happen. Sections 264/265.52(c) require the contingency plan
to describe arrangements and coordination between the facility
and these local authorities. This review might have been
done initially, but any significant changes to a facilitys
operations that cause the contingency plan to be revised
should also be brought to the attention of the local authorities,
and their review of the revised contingency plan should
be conducted when the revised plan is sent to them per §§264/265.53(b).
Finally,
there has been a trend in recent years towards developing
an integrated facility contingency plan, covering all regulatory
(environmental, health, and safety) requirements. These
so-called one plans can be a good idea, but
they are sometimes written by non-RCRA personnel who dont
fully understand the RCRA contingency plan requirements.
Thus, a state RCRA or EPA inspection of the resulting document
may uncover noncompliance with the Part 264/265, Subpart
D or §262.34(d)(5) provisions.
Labeling
violations
By far
the most common labeling violations are hazardous waste
accumulation tanks or containers at generator facilities
not being labeled with the words Hazardous Waste
or containers not being labeled with the 90- or 180-day
accumulation start date. These requirements are found in
§262.34(a)(23) of the RCRA regulations [small
quantity generators get there by reference in §262.34(d)(4)].
Its
not too difficult to comply with the RCRA labeling requirements
for an accumulation tank; just put a big Hazardous
Waste sign or label on the tank and track the start
and end of each accumulation period in a logbook. However,
EPAs guidance says that accumulation start dates should
be marked on tanks, as well as containers.
The
vast majority of NOVs in this area are for improper/missing
container labeling. Make sure your hazardous waste training
and management procedures get your people in the mindset
that 90- or 180-day containers of hazardous waste must be
labeled Hazardous Waste and have the 90- or
180-day accumulation start date on them.
One
of the problems that crops up is that many 90- or 180-day
accumulation containers often begin their lives as satellite
accumulation units. The labeling requirements for satellite
units are different from those for 90- or 180-day containers.
For example, satellite containers do not have to be labeled
Hazardous Waste; they can be labeled with other
words that identify the content of the containers (but they
must have a label on them). Additionally, these containers
are usually dated when the 55-gallon limit is exceeded (for
nonacute hazardous waste). That date of excess satellite
accumulation is not necessarily the same date as the start
of the 90- or 180-day accumulation period, depending on
how long it takes (up to 3 days) for personnel to move it
into the 90- or 180-day accumulation area. Therefore, the
container may have to be relabeled when it is moved into
the 90- or 180-day accumulation area. A Hazardous
Waste label is required, as well as the 90- or 180-day
accumulation start date marking, when that container enters
the 90- or 180-day accumulation area. (However, some facilities
use the date of excess satellite accumulation as the start
of the 90- or 180-day clock. We dont see any problem
with that.)
Failure
to make hazardous waste determinations
Anyone
who generates a solid waste is required by RCRA to determine
if it is a hazardous waste (see §262.11). Yet, when
state or EPA personnel are inspecting a site, they often
find drums or buckets of stuff in warehouses,
maintenance areas, behind buildings, and along fence lines
that nobody at the facility seems to know anything about.
These containers often have no labels on them or the labels
that are on them do not reflect the container contents.
Such orphan materials are usually unneeded or
out-of-date products (e.g., paint, cleaners) or wastes that
someone at the plant (including contractors) wants to get
rid of, but they havent followed plant procedures
for characterizing and storing the waste materials. Usually
in these cases, the inspector will try to determine whether
the material is a solid waste; if it is, and at the discretion
of the inspector, such a facility can be cited for not making
a hazardous waste determination for the solid waste. Numerous
enforcement cases and significant monetary penalties have
resulted from these situations.
In a
case with which we are familiar, a state inspector observed
a facility managing a solid waste stream as nonhazardous.
The inspector asked to see the waste analysis data supporting
the nonhazardous waste determination, but the facility responded
that they had made a knowledge-based determination that
the material was not hazardous. When the inspector then
asked to see the information used to make the knowledge-based
determination, the facility couldnt produce anything.
As a result, the inspector cited the facility for not making
a hazardous waste determination for the solid waste stream.
(The facility subsequently had the material analyzed and
it was indeed nonhazardous, but the NOV for not making a
hazardous waste determination was still valid.) Thus, whenever
knowledge-based determinations are made, they should be
documented.
Ensure
that procedures have been established for your facility
that detail what should happen to materials that are not
needed anymorewho should be contacted, how should
they be characterized if they are solid waste, to where
should they be moved, who should label them, etc. You should
also periodically train your people and remind them of the
potentially costly problem they could create by moving a
drum of stuff out of their area to make it someone elses
problemit could wind up being everyones problem
if an inspector spots it.
Finally,
all hazardous waste determinations for each solid waste
generated at a facility should be documentedwhether
they are made via testing or knowledge.
Improper
tank management
Tanks
used for hazardous waste management are subject to Part
264/265, Subpart J standards. Large quantity generators
operating 90-day tanks get there by reference from §262.34(a)(1)(ii);
small quantity generators 180-day tanks are subject
only to the less-stringent provisions of §265.201 per
reference from §262.34(d)(3).
A number
of requirements in Subpart J could get a facility in trouble,
but the most likely are 1) inadequate or missing secondary
containment for the tank and/or ancillary equipment, 2) failure
to conduct and/or document daily inspections of the tank
and associated equipment, and 3) noncompliance with
the Subpart CC air emission standards.
Land
disposal restrictions violations
The
land disposal restrictions (LDR) in Part 268 of the RCRA
regulations are so complex, that a myriad of noncompliance
issues could crop up. From a hazardous waste generators
perspective, however, the most common source of violations
is LDR paperwork. In many cases, the only way that regulators
can determine if a generator is in compliance with LDR requirements
is by examining copies of the paperwork (notifications and
certifications) required by the regulations. If a generators
LDR paperwork is in order, the likelihood that the facility
will encounter LDR enforcement problems is greatly reduced.
Typical
LDR paperwork problems to watch out for include: