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CEPA REVIEW
Consultations
Comments from the Canadian Water and Wastewater Association
(CWWA) on issues of concern for Municipal Water and Wastewater
Utilities with respect to CEPA 1999
Environment and Health Canada's scoping document positioned
issues in CEPA 1999 from their perspectives. This document
was reviewed and additions made as appropriate to address
CWWA member concerns when considering improvements to CEPA
1999.
Issues of immediate concern to members of the Canadian
Water and Wastewater Association, the national voice of
water and wastewater utilities across Canada, include, but
are not necessarily limited to the following issues. CWWA
looks forward to continued involvement in the Parliamentary
Review process as it unfolds from April 1, 2005 to Royal
Assent and Proclamation of a new or revised CEPA in 2008.
CEPA "toxic"
- although the definition of CEPA toxic creates angst
in the minds of the public through the use of the word
"toxic", we believe that at this time it is
likely the best definition possible. However, there must
be distinction made as to the differences and/or similarities
with "toxic" and "deleterious" substance
as per the Fisheries Act to clarify responsibilities for
municipal owners and operators discharging to the environment;
- CWWA believes there would be value in adding a category
within the definition of CEPA toxic for substances that
may be considered "environmentally harmful"
but not necessarily "toxic" in the normal connotation
of the word "toxic"; This could be useful in
helping to distinguish appropriate control measures.
- the process whereby substances are chosen to undergo
risk assessment and determination of their potential for
Schedule 1 requires clarification. Single substance management
imposes incredible burdens on municipal facilities that
act, not as the polluters, but as the recipients of others'
wastes;
- the determination of "toxicity" must be based
on good science and "reasonable" interpretation
- although laboratory protocols may be an initial determining
instrument, unless they reflect environmental conditions,
they can lead to inappropriate determinations. Across
the board management for a substance that poses a risk
under very specific conditions must be evaluated in development
of a management instrument.
"pollution prevention"
- pollution prevention has different connotations for
different sectors, pollution prevention being more encompassing
for some than others and can be confused with "pollution
control" a term commonly used in the municipal wastewater
services sector. In respect to municipal waste water services,
there needs to be clarification as to where in the wastewater
collection, treatment and discharge elements of these
systems the federal government intends to commence its
application of CEPA and if they do proceed as far upstream
as to dischargers to the sanitary system, what powers
will municipalities be given to enforce in respect to
dischargers to their systems?
- if CEPA is intended to reach up the system e.g. user
responsibility rather than municipal responsibility, then
instruments chosen for substance (or mixtures/whole effluents)
must reflect this in scope, development, duration for
planning and implementation;
- creation of new problems by undertaking another action
(e.g. removal of ammonia may increase nitrogen levels
that may be environmentally more detrimental than ammonia
toxicity);
"reporting" , quality of information, and its
use
- CWWA fully supports the objectives of reporting information
to Environment Canada as this is the only way policies
and legislation can be soundly based, however, a number
of reporting requirements (e.g., NPRI, Environmental Emergency
Regulations, and the proposed Pollution Prevention Planning
Requirements) adds a considerable burden of paperwork
on municipalities and when taken into account with requirements
imposed by provincial and territorial jurisdictions has
to be reduced; harmonization of reporting is proposed
as with Ontario and the Federal government agreement on
air emissions for NPRI;
- reporting for reporting sake is not supported. There
must be QA/QC guidelines for reporting of data, common
sense used in the timing of reporting for various sectors,
rethinking of public access to results to avoid "out
of context" use, and consideration to substance reporting
and what it means e.g. total nitrogen versus nitrate.
"integration and/or harmonization "
- integration and harmonization between governments and
programs would address time lines for municipal governments
to comply on issues related to infrastructure to meet
new instruments. This is particularly important when municipal
planning horizons for infrastructure can be 20 years so
funding and building can't take place to accommodate overly
expeditious federal legislation;
- Time lines for action must take into account other requirements,
such as environmental assessment and approvals applicable
under other federal or provincial/territorial statures.
The following section follows the questions provided section
by section in the consultation document.
SECTION 3: EFFECTIVE DECISION-MAKING
Q 3.1. What are your views on this issue?
Pollution prevention should go up system to the source,
not strictly rest with the owner of the system (e.g. municipal
wastewater systems are not the polluters)
We agree with the precautionary principle but it is often
extremely expensive and non-technically practical when
it comes to large systems or infrastructure needs
We'd like to have transparency but in a timely fashion,
not after the fact as with some of the consultation and
changes to the ammonia and chloramines notices
We support sound science but also urge some common sense
in the approaches derived from scientific solutions, and
a greater reliance on actual environmental observations
and reality
Q 3.2. Should CEPA 1999 provide support for the objective
of keeping-clean-areas-clean? If so, how?
A. we agree that CEPA should support pollution prevention,
BMP and BAT but not at the risk of creating more paperwork
(reporting). The paper burden for municipalities is extreme.
Q 3.3. Does work under CEPA 1999 adequately consider
the precautionary principle and the most vulnerable populations?
A. vulnerable populations could be interpreted as municipal
governments that are under the control of provinces. The
federal government has been working with provinces but
that doesn't necessarily roll down to the municipal level.
We agree that the federal government should not work directly
with municipalities but do have to consider them as extremely
important in many issues.
Q 3.4. Does CEPA 1999 adequately enable effective transparency,
access to information and opportunities for public participation?
A. it may adequately enable transparency but that does
not mean it's happening in a timely fashion. Consultation
is great but must mean true consultation, not "here
it is whether you like it or not" Furthermore, the
transparency must include elements of the regulatory impact
policy with a greater determination of benefits and costs
of any proposed measures.
Q 3.6. Should the Parliamentary review of the Act be
increased from every five years to every seven years?
A. No, in this instance 5 years has been adequate to
identify a number of problems with the implementation
of CEPA 1999. With the shorter time frame we might be
lucky enough to still have some corporate memory within
the departments. In addition, the dynamics of legislative
and policy changes within the federal/provincial/territorial
framework suggest the maintenance of the five year review
cycle.
Q 3.7. If Ministers choose the route of no further action
under CEPA 1999 (i.e. a non-CEPA measure is pursued), should
conditions be put in place to ensure effective accountability
for protection of the environment and human health?
A. accountability is crucial for any situation but the
challenge is to establish a balance between the reporting
of accountability to the actual "doing" of protecting
the environment and human health.
Q 3.8. If a non-CEPA 1999 measure is pursued, should
CEPA 1999 play a backstop role? If so, how can this be done
efficiently?
A. a safety net is required but not a duplication or extensive
overlap of existing provincial/municipal activities.
Q 3.9. Should CEPA 1999 provide the flexibility to tailor
administrative and equivalency agreements to appropriate
circumstances?
A. Yes, in the environmental field, there are often legitimate
differences of approach or expectations between agencies
having common mandates. A strict interpretation of equivalency
can restrict the ability to recognize provincial or territorial
provisions or requirements - an element of considerable
concern to the municipal water and wastewater sector because
of the extent of existing provincial and territorial regulation.
Because recognition of equivalency can reduce paper burdens
the most flexible use of this provision is essential
Q 4.2. Is there a need to improve the reliability of
information reported under NPRI and the administrative efficiency
of the program? If so, what type of changes to CEPA 1999
would you recommend?
A. we believe that there is a useful purpose for the
NPRI but do have concerns with the quality of information
received (e.g. some emission factors used instead of real
data), the quantity required of municipalities, the inappropriate
use of information (e.g. out of context used to prosecute
and misinform the public); the timeliness of reporting
(e.g. industry and municipal reporting simultaneously
when the latter receive substances from the former).
SECTION 5: SOUND SCIENCE AND RESEARCH
Q 5.1. How may current resources and capacity be used
to further develop and coordinate scientific and research
partnerships and activities, in order to advance scientific
objectives which support decision-making under CEPA 1999?
A. get the Wastewater Technology Centre back to a world
class facility and encourage a similar facility for drinking
water technologies, ensure that the mandates include treatment
of residuals whether from treatment processes or the general
management of urban wastes - in all cases ensuring that
the management of the centres includes appropriate guidance
from the affected stakeholders and other policy and legislative
departments. Get back to a science department rather than
a policy machine. Use resources to achieve this.
Q 5.2. How can Environment Canada and Health Canada
most effectively include traditional aboriginal knowledge
in their decision-making processes?
A. bring aboriginal groups to the table sooner in discussions
and encourage a compromise between the usual approaches
to consultation (since this is not usually considered
by First Nations)
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