QUALITY OF LIFE INDICATORS REPORT COMMENTS
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Comments to Quality of Life Indicators Report by Agricultural Commission below - view response to comments |
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VENTURA COUNTY AGRICULTURAL POLICY ADVISORY COMMITTEE July
24, 2002 Board
of Directors SUBJECT: Limits to Growth and Quality of Life in Oxnard, California—Sustainability
Indicators Dear
Board Members: The
Ventura County Agricultural Policy Advisory Committee (APAC) reviewed
the Fall 2001 summary of the sustainability indicators presented in Limits to Growth and Quality of Life in Oxnard, California.
The APAC is comprised of 5 growers appointed by the County Board
of Supervisors to advise them, the County Planning Commission, Local
Agency Formation Commission (LAFCO), and other decision makers regarding
all matters affecting the county’s agricultural resources and the
local agricultural industry. The
APAC discussed the sustainability indicators at their February 13, 2002
meeting, and raised a number of concerns, particularly with the
pesticides indicator. Pesticides Indicator
The discussion of the pesticides indicator
presents a number of misleading statements regarding the use of
pesticides in the county. The
pesticide use reported to the State Department of Pesticide Regulation (DPR)
includes the amount of pesticides applied to public rights-of-way,
structural applications, and landscape maintenance, in addition to
agricultural applications. Those
pesticides used in non-agricultural applications can be identified from
the index of pesticides used by chemical or by commodity included for
each county on the DPR web site; unfortunately, the listings do not
indicate the toxicity of each chemical so that it can be easily
determined by the public whether the use of toxic chemicals is
increasing or decreasing. According to DPR, the amount of pesticides
applied in Ventura County increased from approximately 6.6 million tons
in 1999 to 7.2 million tons in 2000, or an increase of 8.6 percent. The Agricultural Commissioner’s Office determined that this
increase is largely attributable to the use of larger amounts of heavier
oils on citrus and avocado orchards.
Petroleum and mineral oil products that are diluted with water
are increasingly being used by orchard growers as pest-control
alternatives to more toxic chemical sprays.
Oils must be applied more often to be as effective as the more
toxic products. The DPR
data for the top five chemicals used in Ventura County show that while
about 3 million pounds of petroleum and mineral oil were applied in the
county in 2000; during the same period, 1.7 million pounds of methyl
bromide were applied. In
1999, 2.42 million pounds of oil and 2.07 million pounds of methyl
bromide were used. The use
of methyl bromide decreased by 16 percent from 1999 to 2000, due
primarily to the phase-out of the production and importation of the
chemical by 2005, as mandated by the Montreal Protocol. The pesticide sustainability indicator discussion
presents the argument that since the amount by weight of pesticides
applied to Ventura County agriculture is increasing, the use of toxic
chemicals also is increasing. However,
a comparison of the 1999 and 2000 DPR pesticide use data shows that the
application of less toxic but heavier materials such as oils has
actually increased. The
pesticide indicator should be revised to clarify that the use of more
pesticides (by weight) is not the same as the increased use of toxic
chemicals. Further, it
should also be pointed out that growers use certain pesticides due to a
variety of factors, including the lack of less toxic alternatives that
are as effective, the cost of pesticides, and that all pesticides
(including less toxic ones) are not allowed to be used on all
commodities. In addition,
the potential health risks associated with the application of toxic
pesticides can be avoided if they are applied in accordance with the
label requirements and State and federal pesticide regulations.
We commend the pesticide indicator author for recognizing that
the amounts of pesticides used in residential or other private,
non-agricultural applications, although not reported to the DPR, are of
concern due to the excessive amounts used and the lack of knowledge of
potential risks of the persons applying the pesticide. The pesticide indicator also refers to a
non-toxic material called Clandosan, and states that statewide, the use
of non-toxic pesticides is approximately 0.02 percent.
Pesticide use enforcement staff at the County Agricultural
Commissioner’s Office is not familiar with Clandosan, and requests
that the source of this statement be cited.
Does the “0.02 percent statewide” mean that of all the
pesticides used statewide (including non-agricultural applications),
only 0.02 percent are non-toxic materials?
Please clarify. No Discussion of Value Judgements in Summary
The APAC noted that indicators cannot be
developed unless one makes value judgements about what is important to
one’s quality of life. The
summary of sustainability indicators does not describe the value
judgements that the indicators are based on.
The full report, however, does identify goals that are desired by
the authors, and then proposes the indicators to measure whether the
goals have been achieved. The
APAC is concerned that the summary, which was more widely distributed to
the public than the full study, does not identify the goals (value
judgements), and therefore the public is generally unaware of the basis
for the sustainability indicators.
It should also be noted that peoples’ value judgements differ,
based on their experiences and information that has been provided to
them, among other factors. Different
value judgements are acceptable, provided that they are identified so
that the public may decide whether they agree with them. Ratio
of Total Farmland Acreage to Population Indicator What is this indicator really measuring? The goal of this indicator is to establish “ . . . equilibrium between land uses and the number of County residents, and to maintain an appropriate balance between the amount of farmland and the County population.” However, the discussion does not identify what is an “equilibrium” (does that mean ratio?) between land uses (all land uses, not only agriculture?) and the County’s population. Further, what is meant by an “appropriate balance” between the amount of farmland in the county and the County population? Even if the amount of farmland per resident continues to decease in the future, how can it be determined that this is not an “appropriate balance”? Additional population can be accommodated in the county without losing equivalent farm acreage by increasing the density of development that occurs on non-agricultural land. This would be consistent with “smart growth” concepts and the goals of the multi-family housing units, population density, and high density zone changes/permits indicators discussed in the Sustainability Indicators report. Therefore, a ratio of farmland acreage per County resident that decreases over time is not necessarily an adverse occurrence reflecting a trend away from sustainability, as stated in the Sustainability Indicators summary. Farmland can include a variety of different types
of agricultural soils. Is
the intent of this indicator to measure the acreage of
“prime” farmland that is annually converted to other uses or
all types of land identified as farmland by the State Department of
Conservation, Farmland Mapping and
Monitoring Program? According to the Executive Summary, the purpose
of the study effort was to develop indicators to measure quality of life
issues affecting the City of Oxnard.
Therefore, it would have been more appropriate for this indicator
to address the ratio of total farmland acreage (irrigated agricultural
land including prime, statewide importance and unique farmland
identified by the Farmland Mapping
and Monitoring Program) per population within the City’s Area of
Interest. Even with this change, the purpose of this indicator remains
unclear. Ratio
of Total Farmland Acreage to Urbanized Land Indicator Similar to the ratio of total farmland acreage to
population indicator discussed above, the text does not explain what
this indicator is really measuring.
Again, the term “farmland” is not defined. Based on the data
provided, it is obvious that more development in the county is occurring
on non-agricultural land than on farmland.
As a result, a ratio of total farmland acreage to urbanized land
that decreases over time is not necessarily an adverse trend away from
sustainability, as stated in the Sustainability Indicators summary.
It should be noted that the discussion of the value of lemons and
all County commodities in 1998 is not relevant to determining whether
the identified goal is met. Further,
this indicator could be revised to address the ratio of total farmland
acreage to urbanized land within the City of Oxnard Area of Interest, as
discussed above. A more appropriate way to measure whether the
stated goal of retaining “. . . sufficient farmland to allow the
agricultural industry to prosper . . . ” is achieved is to address the
correlation between the amount of land in agricultural production and
agricultural support industries. As
noted in The Value of Agriculture to Ventura County: An Economic Analysis (Ventura County Agricultural Land
Trust and California Coastal Conservancy, 1996), support businesses such
as packinghouses or agricultural management firms thrive and expand when
agricultural production prospers. If
agricultural lands are reduced or productivity declines, support
businesses may have no other option than to close their doors or
relocate to another agricultural area.
The APAC recommends that the Value
of Agriculture study be used as a starting point to develop an
indicator that addresses this correlation and therefore actually
measures the identified goal. Civic
Engagement Indicators The full Sustainability Indicators report
explains that the indicators were developed to measure quality of life
issues in the context of the County’s and Oxnard’s Save Open Space
and Agricultural Resources (SOAR) initiatives (now ordinances).
While the SOAR ordinances may be relevant to the development
indicators, they are not relevant to the environmental and community
health indicators, and therefore the study effort does not appear to
limit the latter by tying them to SOAR.
However, the civic engagement indicators are very artificial and
restrictive because, as indicated on page 15, “they had to have a SOAR
connection”. If the
environmental and community health indicators were not limited in this
manner, why were the civic engagement indicators?
Certainly there are many (and more proactive and effective) ways
that individuals participate in civic activities other than reviewing
environmental impact reports and commenting on SOAR issues at City
Council meetings. Further,
the measurement identified for the indicator concerning persons
reviewing EIRs does not match the goal of the indicator.
The text on page 25 states that the goal is “to increase public
participation in decision making with regard to projects that may
significantly impact the local environment.” This goal is to be measured by the “annual number of
comments, responses, letters or other communications from residents at
public hearings or recorded in [EIRs] prepared for projects in the City
of Oxnard and its sphere of influence that were SOAR related.”
There are a number of projects that could be proposed in or
within the sphere of influence of the City of Oxnard that are consistent
with the City’s SOAR Ordinance (and therefore there is no need to
mention SOAR in comment letters), or there could be substantial numbers
of comments submitted that address a project’s significant
environmental impacts that have nothing to do with SOAR (consistency
with SOAR is not necessarily a project’s most significant issue).
Further, there are ways to measure public participation in the
development review process other than the number of EIR comments
submitted. Just because
there are no development projects that would generate SOAR-related
public comments (or ones that don’t require EIRs) doesn’t mean that
the community is not engaged in civic activities. Similarly, the indicator regarding public
comments at Oxnard City Council meetings is limited by an artificial
connection to the City’s SOAR Ordinance.
Citizen participation could be measured by the number of
individuals attending and/or commenting at City Council meetings, and
the number of letters, e-mails and other communications received by
individual councilmembers and City staff regarding items considered by
the Council, which the discussion of the indicator appears to address.
The connection of the indicator to SOAR is unnecessary and
irrelevant.
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* The Sustainability Indicators report emphasizes
the need to continually monitor and revise the identified indicators,
develop new ones as appropriate, and seek feedback from the community. The evolving nature of indicators is even reflected in the
title of the report. To
this end, the APAC appreciates the opportunity to provide the above
comments so that the indicators can be refined and expanded to better
measure quality of life goals. Sincerely, Charles
Schwabauer CS:jb |
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The Sustainability Council of Ventura County
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