2014
Implementation Guidelines for Processing Applications for Water Distribution
Systems and Mobile Water Distribution Systems
Prepared May 21, 2014 pursuant to Ordinance No.
160 (revised Oct. 30, 2018)
EXECUTIVE SUMMARY AND CONTENTS
The Monterey Peninsula Water Management
District (MPWMD or District) has enacted Rules & Regulations based on a
series of ordinances. These include the
regulation of Water Distribution Systems.
These 2014 Implementation Guidelines are associated with Ordinance No.
160 (adopted April 21, 2014 and effective May 21, 2014), which makes
comprehensive changes primarily to MPWMD Rules 11, 20, 21, 22 and 173. The intent of these Guidelines is to provide
a “road map” for the public and District staff on how various types of water
systems are now regulated. Common
acronyms are highlighted in bold when first used. The following table summarizes how these
Guidelines are organized:
Table E1-- Summary of
Contents
SECTION |
SUBJECT |
NOTES |
|
|
|
|
Executive Summary |
Table E1, Summary of
Contents Table E2, Common
Acronyms |
|
|
|
Section 1.0 |
Introduction |
Attachment 1, Summary
Table and Flowcharts Attachment 2, Figure
of water source areas |
|
|
|
Section 2.0 |
Pre-Application Tasks |
|
Section 2.1 |
Is
System Within the District? |
Link
to map of MPWMD boundary |
Section 2.2 |
County
Health Dept. Permit and Review |
Link
to County Health Dept. website |
Section 2.3 |
State
Well Completion Report |
Describes
required “well log” |
Section 2.4 |
Well
Registration and Metering |
Links
to MPWMD forms and information |
Section 2.5 |
Property/System
Ownership |
Grant
Deeds and other documentation |
Section 2.6 |
Water
Rights Documentation |
Describes
different types of rights |
Section 2.7 |
Environmental
Review |
Describes
CEQA and other environmental laws |
Section 2.8 |
Number
of Parcels Served |
Describes
ramifications of number of parcels |
Section 2.9 |
Estimated
Water Production |
Describes
water production factors |
Section 2.10 |
Application
Forms and Fees |
Attachments 3 and 4,
Application Forms |
|
|
|
Section 3.0 |
Determine Permit
Pathway |
Table 3A, Questions to
Determine Pathway |
Section 3.1 |
Description
of Exemption |
Attachment 5, Monitor
Well Conversion Request |
Section 3.2 |
Description
of Level 1 WDS Permit |
|
Section 3.3 |
Description
of Level 2 WDS Permit |
|
Section 3.4 |
Description
of Level 3 WDS Permit |
|
Section 3.5 |
Other
Related Protocols |
|
|
|
|
Section 4.0 |
Wells Outside of
MPWRS |
|
Section 4.1 |
Greater
than 1,000 feet from MPWRS |
Table 4A provides
summary |
Section 4.2 |
Within
1,000 feet of MPWRS |
Table 4B provides
summary |
|
|
|
Section 5.0 |
Seaside Groundwater
Basin Wells |
Table 5A provides
summary |
|
|
|
Section 6.0 |
Carmel Valley
Alluvial Aquifer Wells |
Table 6A provides
summary |
|
|
|
Section 7.0 |
Non-Well Water
Systems |
Table 7A provides
summary |
|
|
|
Section 8.0 |
Mobile Water
Distribution Systems |
Table 8A provides
summary |
|
|
|
Attachment 1 |
Permit Process
Flowcharts and Table |
Basic requirements and
permit levels |
Attachment 2 |
Figure of water source
areas |
Basic map |
Attachment 3 |
Application form for
Exemption Request |
Cover letter, fee
handout, and form |
Attachment 4 |
Application form for
WDS Permit |
Cover letter, fee
handout, and form |
Attachment 5 |
Monitor Well Conversion
Request Form |
Form and information |
|
|
|
|
|
|
|
|
|
Table E2— Common
Acronyms in Implementation Guidelines
ACRONYM |
DESCRIPTION (many terms are
defined in MPWMD Rule 11) |
|
|
AFY |
Acre-feet per year |
CEQA |
California
Environmental Quality Act |
COE |
Confirmation of
Exemption |
CVAA |
Carmel Valley Alluvial
Aquifer (also called “alluvium”) |
DWR |
State of California
Department of Water Resources |
EIR |
Environmental Impact
Report |
MCEHB |
Monterey County Health
Department,
Environmental Health Bureau |
MPWMD |
Monterey Peninsula
Water Management District |
MPWRS |
Monterey Peninsula
Water Resource System |
NOE |
CEQA Notice of
Exemption |
SGB |
Seaside Groundwater
Basin |
SWRCB |
State Water Resources
Control Board |
WDS |
Water Distribution
System |
|
|
SECTION 1.0, INTRODUCTION
The
Monterey Peninsula Water Management District (MPWMD or District) is a Special District,
similar to a Park District, created by the State Legislature and ratified by
local voters in 1978. It has broad
powers regarding management of local water resources. The State legislation that created MPWMD
gives it the authority to regulate water-producing facilities within its
boundaries. State Water Code Appendix
118-363 states that a written permit from the MPWMD Board is needed to create,
establish, extend or expand a Water
Distribution System (WDS), and that MPWMD may pass ordinances that create
or amend various rules and regulations to guide that process. The primary ordinances that regulate WDS
Permits and exemptions are Rules 20, 21, 22 and 173, though several other rules
apply to water wells. The MPWMD Rules
& Regulations and ordinances passed to date are available on the District
website at:
http://www.mpwmd.net/ (click on “Rules and Regulations” link
for the latest version), or
An overview of pertinent rules and regulations
relating to water wells and WDS is provided on the District website at:
http://www.mpwmd.dst.ca.us/pae/wds/wds.htm
Rule 11 provides definitions for most
capitalized terms found in the MPWMD Rules and in these Implementation
Guidelines.
These Implementation Guidelines are meant to
provide a “road map” to the public and MPWMD staff on how an application for a
permit to create or amend a WDS, Mobile WDS or Confirmation of Exemption will
be processed. These Guidelines are based
on the comprehensive revision of WDS-related rules adopted by the Board on
April 21, 2014 via Ordinance No. 160, which became effective on May 21,
2014. Additional information about
Ordinance No. 160 may be found on the District website at:
http://www.mpwmd.dst.ca.us/asd/board/boardpacket/2014/20140317/13/item13.htm and
http://www.mpwmd.dst.ca.us/asd/board/boardpacket/2014/20140421/16/item16.htm.
These guidelines describe the actions needed
before submitting an application to MPWMD, and how MPWMD will process various
types of applications. Attachment
1 provides an overview of the overall process in flow chart and
tabular formats.
A key designation that is referred to
throughout these Implementation Guidelines is the Monterey Peninsula Water Resource System (MPWRS)[1]. Additional regulation is imposed in the MPWRS
due to the environmentally sensitive and/or legally protected status of these
areas.
The Guidelines refer to certain water source
areas shown in the figure provided as Attachment 2. These areas are described in more detail in
Section 3.0, and many are defined in MPWMD Rule 11:
·
Carmel Valley Alluvial Aquifer (broken
into four subareas for reporting purposes) – roughly, the flat part of Carmel
Valley (on either side of Carmel River) up to San Clemente Dam;
·
Carmel Valley Upland area – the hillsides of
Carmel Valley;
·
Cachagua Creek/Upper Watershed – roughly the area
upstream of San Clemente Reservoir;
·
Seaside Groundwater Basin – roughly, the
19-square mile area bounded by Canyon del Rey, Highway 68, Laguna Seca, Bayonet Golf Course and the Pacific Ocean.
·
Miscellaneous areas – roughly, all other areas, including
Monterey, Jack’s Peak, Pacific Grove, Pebble Beach, Carmel, and Carmel
Highlands.
More
descriptive information about the Seaside Groundwater Basin is provided on the
District website at:
http://www.mpwmd.dst.ca.us/seasidebasin/ord135/QAOrd135091108.pdf.
SECTION 2.0,
PRE-APPLICATION TASKS
Most WDS are based on water wells. Thus, the following sections assume a well is
the source of supply, unless otherwise noted.
Section 7.0 provides instruction for non-well systems and Section 8
summarizes Mobile WDS (trucked water).
The following subsections describe the documentation to complete before
the District will accept an application for a Confirmation of Exemption or a
WDS Permit.
2.1, Confirm Project Is
within MPWMD Boundary
Before an application is submitted to MPWMD for
a WDS Permit, Mobile WDS Permit or Confirmation of Exemption, the applicant
should verify whether the proposed well or property being served is within the
MPWMD. The District includes the cities
of Carmel, Del Rey Oaks, Monterey, Pacific Grove, Sand City, Seaside, plus the
Monterey Peninsula Airport District and unincorporated areas of Monterey
County, including parts of Fort Ord (south of Marina), the Highway 68 corridor
west of Los Laureles Grade, Carmel Valley, Pebble
Beach and the Carmel Highlands. Please
refer to District map website at:
http://www.mpwmd.dst.ca.us/MapGallery/MPWMD_map_1.jpg.
If you are not sure if the project is within
the District, please call 831/658-5621 and request assistance. Large scale maps are available at the
District office to confirm the location of the subject parcel or well.
If the both the well and property are outside
of the District, you do not need to apply to MPWMD. If either the well or property served
are within the District, an application for an exemption or MPWMD permit is
necessary.
2.2, Monterey County
Well Construction Permit and Certification Form
Before MPWMD can consider an application
involving a well, the applicant must first provide a copy of the Monterey
County Well Construction Permit
issued by the Monterey County Health
Department, Environmental Health
Bureau (MCEHB). This County permit
considers specified setback requirements and assesses if there are potential
effects of the new well on neighboring wells and nearby streams, if
applicable. The County permit allows the
well to be drilled, and usually expires in one year. For wells within MPWMD, the County conditions
of approval include the requirement to obtain a WDS Permit or exemption from
MPWMD. The MCEHB has a series of
requirements depending on the number of parcels and people served. For larger projects, the County requires
demonstration of the technical, managerial and financial ability to run a water
system. For more information, please
refer to the MCEHB website at:
http://www.mtyhd.org/index.php/departments-all/item/drinking-water-protection-services-unit.
The County has specific standards for testing
the well, including limited windows of time for potable (drinking water) well
tests in hard rock environments. Thus,
early coordination with County staff is encouraged. Based on the test results for residential
parcels, the MCEHB issues a “Source Water
Quality and Quantity Analysis Certification Form” (or similar letter) that
specifies the gallons per minute accepted as the reliable capacity of the well
along with water quality data. This form
should be submitted as part of the MPWMD application packet as it is used by
MPWMD as evidence of a reliable supply.
Importantly, for any well within 1,000 feet of
the MPWRS, the District has more stringent standards than the County for the
assessment of potential impacts to streamflow.
Also, the County regulation of wells for irrigation use only (<
1,000 gallons per minute) is minimal.
Thus, MPWMD may require additional testing for such wells depending on
the site-specific situation. Applicants
with wells within 1,000 feet of the MPWRS should contact District staff early
in the well planning process to confirm requirements.
2.3, Well Completion
Report
Before MPWMD can consider an application
involving a well, the applicant must first show that the well was properly
completed via a copy of the “Well Completion Report” form (often called a “well
log”) submitted by the licensed driller to the State Department of Water Resources (DWR) and MCEHB. The hydrogeologic information is protected by
state law and may not be shared with other members of the public without the
owner’s consent.
2.4, Well Registered
and Metered
Before MPWMD can consider an application
involving a well, the applicant must first show that the well is properly registered
and metered with MPWMD, which includes an on-site inspection by District
staff. There is currently a $25
registration fee. Links to information
on well requirements, registration and metering is provided on the District
website at:
http://www.mpwmd.net/regulations/wells-water-systems/ (see upper section).
2.5, Recorded Deed to
Property or Other Ownership Documentation
Before MPWMD can consider an application
involving a well, the applicant must first show that he/she owns or co-owns the
well and/or parcel on which the well is located. This must be in the form of a Grant Deed or
equivalent legal document recorded with the Monterey County Recorder with the
County bar code identification number.
If the owner is a trust, the Trustees must be clearly identified. If the
owner is a corporation, additional documentation such as proof of corporate
status in California, portions of Articles of Incorporation that show who is
authorized to sign for the corporation, and/or minutes of a corporation
directors meeting where a representative is authorized to sign the MPWMD
permit.
2.6, Water Rights
Documentation
The MPWMD does not set water rights in
California, but Rule 21-A requires documentation of water rights. For wells on parcels located outside of the
MPWRS, the ownership information
described in Section 2.5 is adequate to show overlying water rights to
percolating groundwater.
Wells within the Seaside Groundwater Basin (SGB) are affected by the Seaside
Groundwater Basin Adjudication and 2006 Superior Court Decision (as
amended). The number of parcels served
affects the type of water right recognized by the Superior Court. Onsite wells that serve one parcel are called
“Alternative Producers” by the Court and have overlying rights to percolating
groundwater. Wells that serve more than
one parcel are called “Standard Producers” and are viewed as having
appropriative rights, which are more restricted, and actually must be reduced
over time through year 2021 according to a schedule in the Court Decision. The amount of production also may affect how
the well is treated by the Court and Watermaster.
Wells within the mapped Carmel Valley Alluvial Aquifer (CVAA or alluvium), unless
demonstrated as hydrogeologically non-alluvial, are
affected by several actions by the State
Water Resources Control Board (SWRCB).
A SWRCB appropriative water right permit or documentation of riparian or
pre-1914 rights must be provided to MPWMD, which is then reviewed by District
Counsel, who confirms in writing whether the documentation is adequate for the
purposes of the WDS Permit. Consultation
with MPWMD staff is suggested for wells within the CVAA.
2.7, Environmental
Review
Several federal and state environmental laws
can affect processing a WDS application, especially if the project location is
within or near sensitive environmental areas such as the CVAA. The federal Endangered Species Act plays a
large role along the Carmel River due to critical habitat for two listed
species (steelhead salmon and red-legged frog).
The primary state law affecting local projects is the California Environmental Quality Act
(CEQA), with which all local and state agencies must comply. More information about CEQA can be found at:
http://ceres.ca.gov/ceqa/guidelines/.
In general, CEQA calls for either a Notice of Exemption (NOE) or an
environmental review document. There are
two types of CEQA Exemptions:
ministerial or categorical.
Ministerial approvals must comply with CEQA Guidelines section 15268 and
15369, and involve little or no personal judgment; approval is based on
objective, measurable criteria. CEQA
Categorical Exemptions are defined in CEQA Guidelines Article 19, sections
15300 through15333. These sections list
a variety of categories such as limited residential or commercial projects of a
certain size on one parcel. Filing of
the NOE is voluntary.
If a project does not meet the CEQA exemption
criteria (e.g., commercial or more complex multi-parcel residential situations,
especially new subdivisions), then the Lead Agency must prepare an Initial
Study to determine which type of environmental document applies – Negative Declaration,
Mitigated Negative Declaration or Environmental
Impact Report (EIR). These entail
public review and comment, hearings and a Notice of Determination issued by the
approving agency.
The type of CEQA compliance by the District
varies with the type of WDS situation and the project-specific environmental
setting. Generally speaking, if the
application meets the criteria for an MPWMD Exemption or a Level 1 WDS Permit,
the water system will likely meet the criteria for a CEQA Ministerial or
Categorical Exemption. MPWMD typically
does not file a NOE for Ministerial Exemptions, but does typically file a NOE
for Categorical Exemptions. For more
complex applications, the District typically relies on the environmental
documents adopted by the CEQA Lead Agency for an approved development project,
which must address water supply and hydrologic impacts. Monterey County or another local jurisdiction
is the CEQA Lead Agency for any development project within their boundary
(e.g., use permit or building permits) and is responsible for preparing the
environmental documents.
If the WDS application is a single-parcel,
single-family residential situation outside of the MPWRS, the applicant does
not need to provide environmental information.
For projects within the MPWRS, or for larger, more complex multi-parcel
projects located outside the MPWRS, the applicant should have coordinated with
the respective planning department before submitting the application to
MPWMD. A WDS application will be
deemed as incomplete if the necessary environmental review documents are not
attached.
2.8, Number of Parcels Served
The legislation that created the District
requires a WDS Permit for systems that serve four or more parcels. The number (and location) of parcels served
may also affect the type of water rights for wells in the Seaside Groundwater
Basin and Carmel Valley Alluvial Aquifer.
2.9, Estimate of Annual Production
For all situations, the applicant should have a
basic understanding of the quantity of water that the potential desired uses on
the parcel(s) would require. As noted in
Section 3.0 below, some WDS Permits outside of the MPWRS do not impose
production limits. However, the
applicant should be very aware of his/her annual and daily needs, the
limitations of his/her water system, and operate the system to minimize
disruption or dewatering of the water source.
For the Seaside Basin, whether the production is 5.0 AFY or greater
affects how the permit will be processed.
The following links from the District website provide means to estimate
potential water use on the property (March 2014, subject to change):
http://www.mpwmd.dst.ca.us/wdd/Forms/Residential%20Factor%20Calculation%20Revised%2020131218.pdf
http://www.mpwmd.dst.ca.us/wdd/Forms/Non-Residential%20Factor%20List%20Revised%2020120701.pdf
http://www.mpwmd.dst.ca.us/wdd/Forms/Water%20Budget%20Requirements_021306.pdf
http://www.mpwmd.dst.ca.us/pae/wds/WDSPermits/WaterFactors_irrigation2009.pdf.
2.10, Application Forms and Fees
The above information described in Sections 2.1
through 2.9 will be part of the application package submitted to MPWMD, and is
used to determine which permit pathway is appropriate. For some situations, additional hydrogeologic
testing information will be required. As
explained in Section 3.0 below, there are four types of application
pathways: Exemption, Level 1 WDS Permit,
Level 2 WDS Permit, and Level 3 WDS Permit.
The information is Section 3.0 is provided to guide the applicant to
choose the proper pathway that matches his/her situation. The applicant should call MPWMD staff for
assistance if he/she is unsure of which pathway to choose. The MPWMD Application Forms are provided as Attachments 3
and 4 and are also on the District
website at:
http://www.mpwmd.dst.ca.us/pae/wds/wds.htm (click on “Exemption
Request Form” or “WDS Application Form.”
Each application is associated with an initial
application fee. The application fee is
based on the best estimate of staff time to process the application, plus
direct costs charged to MPWMD such as District Counsel review of water rights
documents or a deed restriction, hydrogeologic or planning reviews performed by
consultants, filing fees to County Clerk, and recording fees to the County
Recorder. Fees and rates for staff time
are set by MPWMD Rule 60, and may be changed by the District Board from time to
time. The current (May 21, 2014) staff
rate is $95/hour; the current rate for District Counsel is $215/hour. Current consultant fees range from $90 to
$165 per hour. If actual costs exceed
the initial application fee, the applicant must pay the overage before the
Confirmation of Exemption or WDS Permit is finalized. The District provides an accounting of costs
to each applicant. If total costs are
less than the application fee, a refund is provided.
In unusual cases, the actual time to process an
application may greatly exceed the initial fee.
In these situations, staff will review the cumulative total of hours and
expenses accrued each quarter (January, April, July and October). The applicant will be billed if the quarterly
total is more than $500 over the initial fee.
The applicant must pay the overage before staff continues processing the
application. This quarterly billing
policy also avoids a significant fee at the end of the permit process. The Confirmation of Exemption or WDS Permit
is not signed and recorded until all fees are paid.
In summary, before applying to MPWMD, the applicant should
confirm if the well or the property are located within the District, and
have the following documentation: ·
Parcel
map showing location of well and properties to be served ·
Monterey
County Well Construction Permit (fee determined by MCEHB) and
certification of adequate quantity and quality ·
DWR
Well Completion Report ·
MPWMD
Well Registration form ($25 fee) ·
MPWMD
Well Metering Inspection Form signed by District staff ·
Grant
Deed or other ownership documentation ·
Water
rights documentation, if required ·
Environmental
review, if applicable ·
Number
of parcels to be served by each well or other facility ·
Estimated
annual production ·
Signed
Application Form with proper fee.
Section 3.0, Determine
Permit Process Level
This section is intended to help determine
which application process applies to the water system, based on the answers to
the following questions:
·
Is
the system located outside the Monterey Peninsula Water Resource System?
·
Is
the water source located within 1,000 feet of any component of the MPWRS?
·
Is
the water source located within the Seaside Groundwater Basin?
·
Is
the water source located within the Carmel Valley Alluvial Aquifer?
·
How
many parcels are served by the water system?
·
How
much water production is anticipated?
·
Is
the water system based on a well or other type of facility?
These water source areas are defined in MPWMD
Rule 11 and are shown on the map in Attachment 2. The non-MPWRS components in the figure are
the “CVU, CAC and MIS” areas. The
alluvial aquifer is shown as four segments labelled AS1 through AS4. The Seaside Basin is also labelled. The figure is also on the District website
at:
http://www.mpwmd.dst.ca.us/wrd/waterproduction/soucearea2.jpg
Based on the answers to the above questions, the application
would follow one of four pathways: ·
Exemption
·
Level
1 WDS Permit (Basic Non-MPWRS; No System Limits) ·
Level
2 WDS Permit (Basic Seaside Basin; General Adjudication Limits) ·
Level
3 WDS Permit (Project-Specific MPWRS/Other with System Limits).
Due to the many combinations and permutations that
are possible, the different source areas are treated separately in the
following tables and sections. Table 3A below provides the
basic questions that lead to a series of other tables and discussion sections.
Table 3A— Questions to Determine
Permit Pathway
SETTING QUESTIONS |
YES |
NO |
NOTES |
Q1= Is this a
Non-MPWRS Well (e.g., Fractured Rock Well) |
Go
to Table 4A, 4B Section 4.0 |
Go
to Q2 |
MPWRS
and FRW defined in MPWMD Rule 11 (see also page 3) |
Q2= Is this a Seaside
Groundwater Basin (SGB) Well? |
Go
to Table 5A, Section 5.0 |
Go
to Q3 |
SGB
defined in MPWMD Rule 11 |
Q3= Is this a Carmel
Valley Alluvial Aquifer (CVAA) Well? |
Go
to Table 6A, Section 6.0 |
Go
to Q4 |
CVAA
defined in MPWMD Rule 11 (see also page 3) |
Q4= Is this a Non-Well
Situation? |
Go
to Table 7A, Section 7.0 |
Go
to Q5 |
Includes
onsite and offsite rainwater collection; non-potable natural springs;
reclamation, desal plants; dams etc |
Q5= Is this a Mobile
WDS |
Go
to Table 8A and Section 8.0 |
n/a |
Mobile
WDS is water hauled in bulk quantities; MCEHB allows non-potable only for
permanent use |
The District does not distinguish between
non-potable irrigation/pool wells and drinking water (potable) wells in regards
to impact assessments because the same quantity of water is extracted from the
source of supply regardless of eventual treatment and use. The MCEHB or District may impose different
testing requirements and standards for irrigation wells vs. potable wells
depending on the situation.
Importantly, all regulatory paths include the requirement for the applicant to enable the District to physically monitor the wells or other facilities as needed. This is in addition to current requirements to register, meter, and annually report production each water year. The District will continue to monitor the physical situation and make adjustments through future ordinances as needed.
Sections
3.1 through 3.4 below describe the four permit pathways, and provide
examples. Refer to Sections 4.0 through
8.0 for a detailed review of various scenarios for each water source area.
3.1, Exemption
An exemption means that the system does not
need a WDS Permit because it meets one or more of the criteria specified in
MPWMD Rule 20-A or 20-C. Examples are
shown in Tables 2 through 6 below, and include:
·
Replacement
wells or other exemptions listed in Rule 20-C;
·
New
wells located more than 1,000 feet from the MPWRS and serving fewer than four
parcels;
·
New
wells located 1,000 feet or less from the MPWRS and serving fewer than four
parcels, and can demonstrate lack of hydrogeologic connectivity or impact to
the MPWRS;
·
New
Seaside Groundwater Basin wells that produce less than 5.0 AFY and serve one
parcel;
·
Natural
spring in Fractured Rock that provides non-potable supply for onsite landscape
irrigation on one parcel;
·
Onsite
rainwater collection system serving one parcel (Exemption Request is not
required);
·
Mobile
WDS trucked from a source outside MPWMD boundary for use on 3 or fewer parcels,
with documentation showing the supply is lawful (Exemption Request is not
required if less than 55-gallon containers).
Unless otherwise noted in Rule 20, District
staff prepares a Confirmation of
Exemption (COE) report, including (as applicable) the MCEHB Well
Construction Permit number, DWR Well Completion Report number, and
certification of adequate water quality or quantity form or other MCEHB
documentation. System Limits are not
imposed by MPWMD and there is no requirement to assess impacts to Neighboring
Wells (Rule 21-A). The COE also includes
Findings of Approval with cited evidence, and Conditions of Approval that
include a prohibition on water waste, and require access for MPWMD staff to
occasionally monitor the well, among others.
The applicant must sign and notarize a deed restriction that attaches
the COE package along with an Acceptance
of Conditions of Approval Form.
For non-MPWRS wells, the COE states that
Fractured Rock Wells are inherently unreliable as compared to other sources,
and water supply is not guaranteed. The
COE also states that future regulation by MPWMD is possible if monitoring or
other evidence shows substantive changes to the hydrologic setting, water
resource conditions, overdraft etc.
The COE
Application Form is provided as Attachment
3. The
initial application fee is $600.00 based on an estimated seven staff hours,
one hour of Counsel review, plus other direct costs as described in Section
2.10 (based on March 2014 rates).
Monitor Wells:
For exemptions in Rule 20-C that entail replacement of an old well,
MCEHB may require that the old well be properly destroyed in accordance with
specific procedures. One exception is if
MPWMD staff wishes to use the old well as a monitor well. The well owner must initiate this action by
submitting a written request to MPWMD, using the request form provided as Attachment
5, and pay the $25 fee. MPWMD
staff will review the well data to determine if the well location or depth
would provide useful information. If the
answer is yes, MPWMD will request that MCEHB waive the requirement to destroy
the well. A monitor well may not be used
for production purposes. Also, MPWMD
staff must be provided access to the property to install, read and maintain
equipment. The well owner must also pay
a $500 fee for the conversion of the well to a monitor well. The
conversion fee is used to purchase and install water level monitoring
equipment. It is noted that these costs
are significantly lower than the cost of destroying a well.
Older
Well Tests: The District will accept older well tests so
long as they are acceptable to MCEHB (i.e., previous test meets current MCEHB
standards, the well is physically viable, and no substantive changes have
occurred in the water resource setting).
3.2, Level 1 WDS Permit
(Basic Non-MPWRS; No System Limits)
A Level 1 Permit is for a system located outside
of the MPWRS with correlative water rights that would not have an adverse
effect on the MPWRS, but does not meet any of the criteria for an exemption
specified in MPWMD Rule 20-A or 20-C.
Examples of Level 1 WDS Permits include:
·
Wells
located more than 1,000 feet from the MPWRS and serving four or more parcels;
·
Wells
located 1,000 feet or less from the MPWRS and serving four or more parcels,
which can demonstrate lack of hydrogeologic connectivity or significant adverse
impact to the MPWRS;
·
Rainwater
collection system that serves one or more offsite parcels for irrigation only;
·
Natural
spring in Fractured Rock that provides non-potable supply for landscape
irrigation to one or more offsite parcels;
·
Mobile
WDS trucked from a source located more than 1,000 feet outside of the MPWRS.
The basic application materials described in
Section 2.0 would be required in addition to information specified in Rule 21,
as applicable. A key element of the
Level 1 Permit is that System Limits (production and connections) are not
imposed. Because of the assumed
correlative rights, the applicant is not required by MPWMD to monitor or assess
the potential effect of the new well on Neighboring Wells. Documentation by the MCEHB on the adequacy of
the well quantity and quality is accepted by MPWMD as evidence of reliable
supply; additional hydrogeologic analysis above and beyond that already
performed for the MCEHB is not required.
The Rule 22 Findings, Minimum Standards, and Conditions of Approval that
are associated with System Limits or impacts to Neighboring Wells are
waived. It is noted that MCEHB has
increased its review of impact to nearby wells and sensitive streams as part of
its Well Construction Permit issuance.
The Application
Form for a Level 1 WDS Permit is provided as Attachment
4, and reflects the above requirements. The
initial application fee is $1,200 (May 2014) based on an estimated ten
staff hours, one hour of Counsel review, plus other direct costs as described
in Section 2.10.
3.3, Level 2 WDS Permit
(Basic Seaside Basin; General Adjudication Limits)
Level 2 would be for Seaside Groundwater Basin
situations where production is less than 5.0 AFY and for certain single-parcel
situations where production is 5.0 AFY or more.
The 5.0 cutoff value is chosen because the Superior Court in the SGB
Adjudication Decision determined that production less than 5.0 AFY would have a
nominal effect on the Basin. Examples of
Level 2 Permits include:
·
SGB
wells that produce less than 5.0 AFY and serve two or more parcels;
·
SGB
wells that produce 5.0 AFY or more and serve only one onsite parcel
(Alternative Producer), with a designated production amount in the Court
Decision or written permission from the SGB Watermaster.
·
Mobile
WDS trucked from a source within the Seaside Basin if compliant with the
Adjudication Decision.
The basic application materials described in
Section 2.0 would be required in addition to information specified in Rule 21,
as applicable. A key element of the
Level 2 Permit is that System Limits (production and connections) are
simplified to be either less than 5.0 AFY, or the value specified for the property
in the Adjudication Decision, or a site-specific Watermaster
approval. Notably, the production limit
for multi-parcel Standard Producers will account for the Court-ordered
reductions through year 2021. If the
applicant has designated water rights, he/she is not required by MPWMD to monitor
or assess the potential effect of the new well on Neighboring Wells. Documentation by the MCEHB on the adequacy of
the well quantity and quality is accepted by MPWMD as evidence of reliable
supply. Additional hydrogeologic analysis above and beyond that already
performed for the MCEHB is not required.
If the applicant does not have designated water rights in the
Adjudication, MPWMD may require additional hydrogeologic testing to demonstrate
that approval would not “create or exacerbate an existing overdraft” (Rule
22-C-4). The Rule 22 Findings, Minimum
Standards, and Conditions of Approval that are associated with System Limits or
impacts to Neighboring Wells would incorporate the Adjudication determinations.
CEQA compliance by MPWMD differs in the SGB as
the Superior Court’s environmental determinations in the Adjudication Decision
override the normal CEQA process. Thus,
separate CEQA review by MPWMD is not necessary for parcels included in the
Adjudication.
The Application Form for a Level 2 WDS Permit
is provided as Attachment 4, and reflects the above
requirements. The initial application fee is $1,200 (May 2014) based on an
estimated ten staff hours, one hour of Counsel review, plus other direct costs
as described in Section 2.10.
3.4, Level 3 WDS Permit (MPWRS/Other with
Specific System Limits)
Level 3 is the highest review level and
involves the imposition of System Limits (production and connections) as well as
possible hydrogeologic testing and assessments above and beyond that required
by MCEHB, depending the situation. The
testing procedures are provided on the District website at:
http://www.mpwmd.dst.ca.us/pae/wds/WDSPermits/WellAssessProcedures_ver3edit_14sep05.pdf.
Examples of Level 3 WDS Permits include:
·
Non-MPWRS
wells within 1,000 feet of the MPWRS that have the potential for a significant adverse
effect to the MPWRS above a certain production level;
·
Seaside
Groundwater Basin wells that produce 5.0 AFY or more (with written permission
from the Seaside Basin Watermaster), and serve more
than one parcel;
·
All
situations in the mapped Carmel Valley Alluvial Aquifer unless the well log
demonstrates that the water source is non-alluvial and there is not
hydrogeologic connectivity to the CVAA;
·
Direct
diversion from any stream within the MPWRS;
·
Fractured
Rock spring used for any potable (drinking water) offsite use, or commercial
use;
·
Dams,
desalination plants, reclamation facilities and all water projects that require
an EIR;
·
Mobile
WDS trucked from a source within the MPWRS.
The
basic application materials described in Section 2.0 would be required in
addition to information specified in Rule 21, as applicable. A key
element of the Level 3 Permit is that System Limits (production and
connections) are imposed, based on the physical capacity of the well and the
potential environmental impacts to the MPWRS. Additional hydrogeologic
analysis above and beyond that already performed for the MCEHB will be required
in most cases. In some situations, documentation by the MCEHB on the
adequacy of the well quantity and quality may be accepted by MPWMD as evidence
of reliable supply. The Rule 22 Findings, Minimum Standards, and Conditions of
Approval that are associated with System Limits will be in effect.
An assessment of a well-based water system on
Neighboring Wells will be required by MPWMD unless the application demonstrates
that the property falls into one of the following categories:
·
Correlative
water rights exist with neighboring parcels (non-MPWRS);
·
Riparian
or Pre-1914 rights are demonstrated to the satisfaction of MPWMD Counsel
(CVAA);
·
Appropriative
water right or domestic registration is issued by SWRCB (CVAA);
·
Seaside
Basin Adjudication specifies water rights;
·
Superior
water right to those of Neighboring Wells is demonstrated.
Demonstration of CVAA water rights for the
purpose of the MPWMD permit typically entails a formal title search, copies of
all relevant deeds and a compilation of water rights transfers. MPWMD Counsel reviews the submitted
information and issues a memorandum of acceptance or rejection. Examples are available for review at the
District office.
The Application Form for a Level 3 WDS Permit
is provided as Attachment 4, and reflects the above
requirements. The initial application fee is $3,000 (May 2014) based on an estimated
20 staff hours, three hours of Counsel review, several hours of consultant time
(if additional hydrogeologic tests are needed) plus other direct costs as
described in Section 2.10. A Level 3
application has the highest probability of being significantly more costly than
the initial application fee, especially if a public hearing before the MPWMD
board is necessary and/or extensive staff response to public comments is
required.
3.5, Other Related
Protocols
This section summarizes District procedures
that may relate to all permit pathways described above.
Board Review:
The District Board has designated staff to administratively handle all
applications except complex, controversial or large projects, especially if
located within or near the MPWRS. If
there is any question, the General Manager will consult with the MPWMD Board
Chairperson and Vice Chair. All staff
decisions are posted weekly on the District website under “Appealable
Decisions” and all staff decisions can be appealed to the Board pursuant to
Rule 70. The website link with the
recent staff action and appeals forms is found at:
http://www.mpwmd.dst.ca.us/wdd/Appeals/appeals.htm.
Coordination with County Agencies: MPWMD staff regularly coordinates and
consults with MCEHB, the Monterey County Water Resources Agency, and Monterey
County Planning Department regarding well-related regulatory issues. The District also regularly convenes its
Technical Advisory Committee, made up of planning staff from all jurisdictions,
to advise them of changes in District rules that may affect issuance of use
permits or building permits. The goal is
to avoid duplication of effort and ensure consistent direction to applicants,
thereby streamlining the permitting process.
SECTION 4.0, WELLS OUTSIDE OF MPWRS
This section reviews how wells outside of the
MPWRS are treated. These wells are often
referred to as “Fractured Rock Wells” or “hard rock” wells. Key factors include whether the distance is
greater than 1,000 feet from the MPWRS, the degree of connectivity to any
component of the MPWRS, and the number of parcels served. Table
4A provides a summary of the different non-MPWRS well scenarios.
Table 4A— Summary of
Non-MPWRS Well Scenarios
SYSTEM TYPE |
LOCATION |
NOTES |
|
|
>1,000 feet
from MPWRS |
<1,000
feet from MPWRS |
MPWRS=
Monterey Peninsula Water Resource System, defined in Rule 11 (see also page
3). |
Single Parcel
Connection System (SPCS) |
Exemption |
Exemption or Level 1
or 3 WDS Permit |
SPCS=
well(s) are located on, overlie and serve one Legal Parcel. If <1,000
ft., action depends on hydrogeologic connectivity and potential effect to
MPWRS. |
Multiple-Parcel Connection System serving 2
or 3 Parcels |
Exemption |
Exemption or Level 1
or 3 WDS Permit |
If
<1,000 ft., action depends on hydrogeologic connectivity and
potential effect to MPWRS. |
Multiple-Parcel
Connection System serving 4 or more Parcels |
Level 1 WDS Permit |
Level 1 or 3 WDS Permit |
If
<1,000 ft., action depends on hydrogeologic connectivity and
potential effect to MPWRS. |
4.1, Wells Located More than 1,000 feet from
MPWRS
Wells located more than 1,000 feet from the
MPWRS would be either exempt or a Level 1 WDS Permit, depending on the number
of parcels served. There would be no
production limits imposed.
4.2, Wells Located Within 1,000 feet of MPWRS
For wells located 1,000 feet or less from the
MPWRS, District staff would assess if there is potential for adverse impact to
any component of the MPWRS, based on well logs and other submitted information
such as the amount of production. Table 4B summarizes the
questions used to determine how a well within 1,000 feet of the MPWRS should be
treated.
Table 4B— Determine
Permit Level for Wells within 1,000 Feet of MPWRS
QUESTIONS |
NO |
YES |
NOTES |
Q1= Is there any
hydrogeologic connectivity to MPWRS based on well log and other data? |
Exempt
or Level 1 WDS Permit |
Go
to Q2 |
Level
1 WDS Permit is for four or more parcels.
|
Q2= Is there
potential for adverse effect to MPWRS based on hydrogeologic calculations? |
Level
1 WDS Permit |
Go
to Q3 |
Based
on calculations; additional hydrogeologic testing may be required by MPWMD to
confirm potential for impact. |
Q3= Is there
potential for significant adverse effect to MPWRS based on additional testing
or analysis? |
Level
1 WDS Permit |
Go
to Q4 |
Must
define trigger for significant adverse effect. |
Q4= Can potential
adverse effect be reduced to less than significant by reducing the production
amount? |
GO
to Q5 |
Level
3 WDS Permit |
Permit
would impose lower production limit based on data showing less than
significant effect. |
Q5= Are other
mitigation measures available to offset impacts? |
Deny
application |
Level
3 WDS Permit |
Permit
would impose additional conditions to lessen effect. |
SECTION 5.0, SEASIDE GROUNDWATER BASIN
WELLS
This
section reviews how wells within the Seaside Groundwater Basin, as defined in
Rule 11, are treated. Key factors
include whether production is 5.0 AFY or more, and the number of parcels
served. As noted in Section 2.6 above,
the number of parcels served affects the type of water rights specified by the
SGB Adjudication Decision. Table 5A below provides a
summary of the different SGB well scenarios.
Table 5A— Summary of Seaside Groundwater Basin
Well Scenarios
SYSTEM TYPE |
PRODUCTION |
NOTES |
|
|
< 5.0 AFY |
5.0+ AFY |
5.0
AFY trigger set by Superior Court in Adjudication Decision; production below that
amount is deemed as less than significant. |
Single-Parcel
Connection System (SPCS) with overlying right = “Alternative Producer” |
Exemption |
Level 2 WDS Permit |
SPCS=
well(s) are located on, overlie and serve one Legal Parcel. If 5.0+ AFY, need
Watermaster approval if not already on list in
Court Decision. |
Multiple-Parcel Connection System serving 2
or 3 Parcels with appropriative rights= “Standard Producer” |
Level 2 WDS Permit |
Level 3 WDS Permit |
All
Standard Producers need Watermaster approval if not
already on list in Court Decision. |
Multiple-Parcel
Connection System serving 4 or more Parcels with appropriative rights=
“Standard Producer” |
Level 2 WDS Permit |
Level 3 WDS Permit |
All
standard producers need Watermaster approval if not
already on list in Court Decision. |
As noted in Section 2.6 above, owners of wells
that serve more than one parcel are called “Standard Producers” and their
production is reduced over time to meet the natural safe yield, as specified by
the Court. The Adjudication Decision
requires a 10% reduction in production from the 2006 baseline every three years
through 2021, according to a schedule in the Court Decision. The District applies this formula to the
production limit allowed in the WDS Permit unless there are overriding factors
specified in the Adjudication Decision.
SECTION 6.0, CARMEL VALLEY ALLUVIAL
AQUIFER WELLS
This section reviews how wells within the
mapped Carmel Valley Alluvial Aquifer (CVAA), as defined in Rule 11, are
treated. As noted in Section 2.6 above,
the number and location of parcels served affects the type of water rights
specified by the State Water Resources Control Board. Table
6A below provides a summary of the CVAA well scenarios.
Table 6A—Summary of
Carmel Valley Alluvial Aquifer Well Scenarios
SYSTEM TYPE |
NOTES |
All Single and
Multiple-Parcel Connection Systems (well or direct diversion) |
Level 3 WDS Permit |
Wells in mapped CVAA
shown to be non-alluvial based on the DWR Well Completion Report |
Treated as non-MPWRS
within 1,000 feet (See Table 2) |
The CVAA is highly regulated as it supports two
federally listed threatened species (steelhead salmon and red-legged frog) and
is critical habitat for these species.
Because the CVAA is typically very productive as compared to other
sources of supply, production limitations would be based more on the impact to
the CVAA/critical habitat rather than the ability of the well to produce
adequate supply. All wells that extract
water from the CVAA are Level 3 WDS Permits with System Limits, which could
potentially incorporate limits imposed by the SWRCB for appropriative rights
(e.g., season and amount of diversion, storage etc). Property owners with riparian rights must
still be aware of the Endangered Species Act and the Public Trust
Doctrine. The critical habitat component
overrides CEQA Categorical Exemptions that might normally apply (see Guidelines
Section 15300.2, Exceptions).
Because of concern about the impact to the CVAA
and critical habitat, as expressed by letters from the National Marine
Fisheries Service and California Department of Fish and Wildlife, the District
Board adopted a policy to guide processing of WDS Permits in the CVAA. This protocol, along with a supporting
legal analysis of the agency letters, is provided on the District website at:
http://www.mpwmd.dst.ca.us/pae/wds/WDSPermits/WDSMemo3.pdf
It
is noted that some wells within the mapped CVAA are shown to be non-alluvial
based on the well log. For example, the
well may perforate areas below a shallow alluvial zone, especially near the
boundary of the CVAA. In those cases, the
well is treated as if it is an upland well within 1,000 feet of the MPWRS.
SECTION 7.0, NON-WELL SITUATIONS
This section reviews how systems based on
facilities other than water wells are treated.
Examples include many possibilities, ranging from simple onsite and offsite
rainwater collection, to non-potable natural springs to major projects such as
wastewater reclamation, desalination plants, or dams. Table
7A below provides a summary of the non-well scenarios.
Table 7A— Summary of
“Non-Well” Scenarios
SYSTEM TYPE |
PROCESS |
NOTES |
Rainwater collection
for onsite use (irrigation only) |
Exemption |
Typically
entails above or below-ground cisterns or tanks. Exemption Request not required. |
Rainwater collection
for offsite delivery |
Level 1 WDS Permit |
Service
to 1 or more offsite parcels |
Fractured Rock spring
for onsite use (non-potable only) |
Exemption |
Inspect
to confirm it is a naturally occurring seep, not a tributary |
Fractured Rock spring
for onsite potable use (drinking water)
|
Level 1 WDS Permit |
Inspect
to confirm it is a naturally occurring seep, not a tributary |
Fractured Rock spring
for non-potable offsite use (1 or more offsite parcels) |
Level 1 WDS Permit |
Inspect
to confirm it is a naturally occurring seep, not a tributary |
Fractured Rock spring
for any offsite or commercial potable use |
Level 3 WDS |
Inspect
to confirm it is a naturally occurring seep, not a tributary; coordinate with
Health Dept. |
Direct diversion from
any stream or named tributary within MPWRS |
Level 3 WDS Permit |
Must
coordinate with other state and federal laws that protect public trust
resources. Special conditions of
approval are likely. |
Dam, desalination
plant, reclamation, or any water supply project needing an EIR |
Level 3 WDS Permit |
Must
coordinate with other agencies regarding environmental review. Special conditions of approval are likely. |
SECTION 8.0, MOBILE WATER DISTRIBUTION
SYSTEMS
This section reviews how Mobile WDS (water
hauled in trucks in bulk quantities), as defined in Rule 11 and Rule 173, are
treated. A key factor is whether the
source of supply is within the District boundary or not. For sources outside of
the District, a written confirmation from the governmental agency that manages
the water resource is required. Only
non-potable use (e.g., landscape irrigation, swimming pool filling) is allowed
pursuant to MCEHB rules. Trucked potable
(drinking water) supply would only be considered in a short-term emergency (30
days or less) and is not allowed as a sustained, long-term method of
supply. Table 8A below provides a summary of the non-well
scenarios.
Exportation
of water outside of the District as part of a Mobile WDS is prohibited.
An
Exemption Request is not required for State-licensed commercial carriers that
deliver water in containers less than 55 gallons (e.g., Culligan,
Alhambra, etc.).
Table 8A— Summary of
Mobile WDS Scenarios
SYSTEM TYPE |
WATER SOURCE LOCATION |
NOTES |
|
|
Within MPWMD |
Outside MPWMD |
MCEHB
does not allow permanent potable Mobile WDS unless emergency drinking water supply. |
Service to less than
4 Parcels for construction, irrigation or pool use |
Level 1, 2 or 3 WDS
Permit |
Exempt |
For
sources within MPWMD, permit level depends on well location and impacts. Severe restrictions exist for sources
within the MPWRS. For sources outside
MPWMD, system is exempt if documentation shows the supply is lawful. |
Service to 4 or more Parcels for
construction, irrigation or pool use |
Level 1, 2 or 3 WDS
Permit |
Level 1 WDS Permit |
Same
as above except there is no exemption for 4 or more parcels. |
Service to
jurisdictions for public space irrigation |
Level 1, 2 or 3 WDS Permit |
Level 1 WDS Permit |
Same
as above; no exemptions for 4 or more parcels. |
Emergency drinking
water service |
Level 1, 2 or 3 WDS
Permit |
Level 1 WDS Permit |
See
Rule 173; drinking water may be trucked only in a short-term emergency (30
days or less). Severe restrictions
exist for sources within the MPWRS.
Coordination with Health Dept. |
[1] The Monterey Peninsula Water Resource System (MPWRS) is defined as the “surface water in the Carmel River and its tributaries, Groundwater in the Carmel Valley Alluvial Aquifer which underlies the Carmel River, and Groundwater in the Seaside Groundwater Basin” (MPWMD Rule 11). The named Carmel River tributaries are defined in Rule 11 under “Sensitive Environmental Receptors.”