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HomeMy WebLinkAbout1000-80.-5-2.1A4
LWRP CONSISTENCY ASSESSMENT FORM
INSTRUCTIONS
1. All applicants for permits* including Town of Southold agencies, shall
complete this CCAF for proposed actions that are subject to the Town of
Southold Waterfront Consistency Review Law. This assessment is intended to
supplement other information used by a Town of Southold agency in making a
determination of consistency. *Except minor exempt actions including
Building Permits and other ministerial permits not located within the
Coastal Erosion Hazard Area.
2. Before answering the questions in Section C, the preparer of this form
should review the exempt minor action list, policies and explanations of
each policy contained in the Town of Southold Local Waterfront
Revitalization Program. A proposed action will be evaluated as to its
significant beneficial and adverse effects upon the coastal area (which
includes all of Southold Town).
,ECEIVE
MAR 2 5 20]3
Southold Town
Board of Trustees
3. If any question in Section C on this form is answered "yes", then the
proposed action may affect the achievement of the LWRP policy standards and
conditions contained in the consistency review law. Thus, the action should
be analyzed in more detail and, if necessary, modified prior to making a
determination that it is consistent to the maximum extent practicable with
the LWRP policy standards and conditions. If an action cannot be certified
as consistent with the LWRP policy standards and conditions, it shall not be
undertaken.
A copy of the LWRP is available in the following places: online at the
Town of Southold's website (southoldtown.northfork.net), the Board of
Trustees Office, the Planning Department, all local libraries and the Town
Clerk's office.
B. DESCRIPTION OF SITE AND PROPOSED ACTION
Peter Cosola: replace storm damaged bulkhead with vinyl bulkhead, 20' returns, splash pad and
non-turf area landward of bulkhead. Restore storm damaged vegetation. Upper deck has CO and
requires no work. Lower deck in non-turf area is existing and will be replaced, as needed, due to
bulkhead construction. Steps to beach reconstructed as needed due to bulkhead work.
SCTM# 1000- 80-05-2.1
430 West Shore Drive, Southold ~
The Application has been submitted to (check appropriate response): t~ (q,,pv 'q ~
Town Board
1.
__ Planning Dept. Building Dept. Board of Trustees __ _
Category of Town of Southold agency action (check appropriate
response):
(a) Action undertaken directly by Town agency (e.g. capital
construction, planning activity, agency regulation, land transaction) __
(b) Financial assistance (e.g. grant, loan, subsidy) __
(c) Permit, approval, license, certification:
X
Nature and extent of action: Peter Cosola
replace storm damaged bulkhead with vinyl bulkhead, 20' returns, splash pad and non-turf area
landward of bulkhead. Restore storm damaged vegetation. Upper deck has CO and requires no
work. Lower deck in non-turf area is existing and will be replaced, as needed, due to bulkhead
construction. Steps to beach reconstructed as needed due to bulkhead work (exempt from
LWRP).
Location of action:430 West Shore Drive, Southold
Site acreage:.5 acre
Present land use: residential- existing structures built 1950's; preexisting bulkhead;
upland structures (decks) have CO's
Present zoning classification: r-40
If an application for the proposed action has been filed with the Town of
Southold agency, the following information shall be provided:
(a) Name of applicant: Peter Cosola
(b) Mailing address:430 West Shore Drive, Southold
(c) Telephone number: Area Code ( 917 ) 972-1589
(d) Application number, if any:
Will the action be directly undertaken, require funding, or approval by a
state or federal agency?
Yes No X If yes, which state or federal agency:
DEVELOPED COAST POLICY
Policy 1. Foster a pattern of development in the Town of Southold that
enhances community character, preserves open space, makes efficient use of
infrastructure, makes beneficial use of a coastal location, and minimizes
dverse effects of development. See LWRP Section III - Policies; Page 2 for
evaluation criteria.
XYes No Not Applicable
property improved with a residence, cantilevered upper deck and small platform deck landward
of bulkhead. Existing bulkhead was damaged by Sandy storm.
Attach
additional sheets if necessary
Policy 2. Protect and preserve historic and archaeological resources of the
Town of Southold. See LWRP Section III - Policies Pages 3 through 6 for
evaluation criteria
Yes No XNot Applicable
Attach additional sheets if necessary
Attach
Policy 3. Enhance visual quality and protect scenic resources throughout
the Town of Southold. See LWRP Section III - Policies Pages 6 through 7 for
evaluation criteria
XYes No Not Applicable
all structures built prior to zoning, upper deck built in 1984 with CO.
additional sheets if necessary
NATURAL COAST POLICIES
Policy 4. Minimize loss of life, structures, and natural resources from
flooding and erosion. See LWRP Section III - Policies Pages 8 through 16 for
evaluation criteria
XYes No Not Applicable
existing bulkhead will be replaced. Bulkhead protected property from storm.
Attach
additional sheets if necessary
Policy 5. Protect and improve water quality and supply in the Town of
Southold. See LWRP Section III - Policies Pages 16 through 21 for evaluation
criteria
Yes No Not ApplieableX
Attach
additional sheets if necessmy
Policy 6. Protect and restore the quality and function of the Town of
Southold ecosystems including Significant Coastal Fish and Wildlife Habitats
and wetlands. See LWRP Section III - Policies; Pages 22 through 32 for
evaluation criteria.
XYes No Not Applicable
Attach
property will be restored after storm, vegetated areas will be replanted and maintained.
additional sheets if necessary
Policy 7. Protect and improve air quality in the Town of Southold. See LWRP
Section III - Policies Pages 32 through 34 for evaluation criteria. See
Section III - Policies Pages; 34 through 38 for evaluation criteria.
Yes No XNot Applicable
Attach
additional sheets if necessary
Policy 8. Minimize environmental degradation in Town of Southold from
solid waste and hazardous substances and wastes. See LWRP Section III -
Policies; Pages 34 through 38 for evaluation criteria.
Yes No XNot Applicable
PUBLIC COAST POLICIES
Policy 9. Provide for public access to, and recreational use of, coastal
waters, public lands, and public resources of the Town of Southold. See LWRP
Section III - Policies; Pages 38 through 46 for evaluation criteria.
Yes No Not Applicable
all structures existing landward of bulkhead area between Mean Low Water and Mean
High Water is not affected.
Attach
additional sheets if necessary
WORKING COAST POLICIES
Policy 10. Protect Southold's water-dependent uses and promote siting of new
water-dependent uses in suitable locations. See LWRP Section III - Policies;
Pages 47 through 56 for evaluation criteria.
Yes No Not Applicable
Attach
additional sheets if necessary
Attach
Policy 11. Promote sustainable use of living marine resources in Long
Island Sound, the Peconic Estuary and Town waters. See LWRP Section III -
Policies; Pages 57 through 62 for evaluation criteria.
XYes No Not Applicable
all structures landward of Town waters.
additional sheets if necessary
Attach
Policy 12. Protect agricultural lands in the Town of Southold. See LWRP
Section III - Policies; Pages 62 through 65 for evaluation criteria.
Yes No X Not Applicable
additional sheets if necessary
Policy 13. Promote appropriate use and development of energy and mineral
resources. See LWRP Section III - Policies; Pages 65 through 68 for
evaluation criteria.
Yes No XNot Applicable
</div>
PATRICIA C. MOORE
Attorney at Law
51020 Main Road
Southold, New York 11971
Tel: (631) 765-4330
Fax: (631) 765-4643
Margaret Rutkowski
Betsy Perkins
Secretaries
March 25, 2013
Southold Town Trustees
P.O.Box 1179
Southold Town Hall
Main Road,
Southold, NY 11971
Re: 1000-80-05-2.1 (Cosola)
Dear President King
and Board:
Enclosed is a wetland permit application to replace 100' linear feet of storm damaged bulkhead
with vinyl bulkhead, 20' returns and Gl 0' splash pad landward of bulkhead.
The upper deck (18.25' x 27' ) is existing and has a certificate of occupancy which is enclosed.
The stairs to the beach will be replaced, as needed, due to the bulkhead reconstruction.
lower deck (18'x 7')is landward of the bul ~khe~/aand is in~e "non-turf,area" behind the bulkhead.
The
The owner uses this area (which is seaward o£~fhe bank) to store l~s children s kayaks, beach chairs and
toys, the existing wood bench and small v0od retaining wall is l~ndward of the bulkhead. The area
landward of the bulkhead is flat and will/be maintained ~s a. nonpurf area behind the bulkhead. The
owner wishes to retain this area with deciding. The decking is "pervious" but if the Board prefers the
grate material over the splash pad, Mr. Cb~,ola is willing to ~re4flace the wood decking with the grated
material. The bank behind the existing wood~a~ll/b6nch will be re-vegetated and restored (pre-
storm conditions)
Enclosed for your file are the following documents:
Trustee application for wetland permit
A copy of photographs of the pre-storm bulkhead, retaining wall, decks and bench.
The owner does not intend to proceed with the previous application as it does not reflect his
current plans. We can either abandon the previous application or we will allow it to lapse.
If you need anything else please do not hesitate to contact me.
~ ' 'aC. Moore
cc:Mr. Cosola
83/85/2012 11:32 63176526~ CDRCORAN NF PAGE 81/82
FORM NO.~4
TOWN OF SOUTHOLD
BUILDING D£PAR~MENT
Office of the Building Inspector
Town Hall
Southold, N.Y,
Certificate Of Occupancy
No. Z1~8 July 31
............. Date .
THI~ CERTIFIES that the buildin~..D.e, c..k..Rd. ~ .i .t~i,q L~. J;.o.. q ~ ~-At~ ~,l~ g. ,h U ;L i~L/, n g ......
LoemtiunofP~ope~ty ~30 West 3hore Drive
Coun~ T~ ~a~ No. lO00 ~eo~ion .q~ ~ ........ Block . .N3 ........... Lot...~0~ ...........
b"ubdivi~io~. ~syclon
.............................. Filed Mnp No ......... ]Lo~ No. ~.l.-.~t .......
con£orms substunfi~ly ~ the Appll~tion Eot Buildin~ ~e~it ~e~oEo~
~/~3 ~/~pu ntt w~chB ildi gP~fitN 1~1~
..................... ~19, I~a 0 ~ ~ O ...................
..................... ~ was iSSUe, ~d ~onf0~S ~O ~ of th~ roq~r~s
of the ap~li~bl, pro~sions of ~e hw. ~ oc~upancF for w~0h i~s c~i~l~ is ~d is .........
~e~ficatei~J~ucd to D. ANN~NOS
of ~O afor~a/d building.
~uffo~ County De~t of H~lth App~l ....... ~<~ ...........
~RWR~sRS ~R~ NO ............... ~.~ ...............................
Building Inspector
03/05/2012 11:32 531765; CORCORAN NF PAGE 02/02
TOV~N OF ~OUTHOLD
TOWN HAM~
$OUTHOLD, N. Y,
BUILDING P £P.J~.rr
(THIS PERJVIIT MUST BE KEPT ON THE PREMISES UNTIL FULL.
CC~vIPLETION OF THE WORK AUTHORIZED)
Permission i~ hereby gronted to.'
........... i.-~...~...~..~.~./~.~.~ ..........
......... ......
...... ..,~,~-_z~...~...:....Z........,.~.zo~-o
~' ........... ,~ ........ · ~ . .
..................................... ~ ......... r~.~ ~
~ ,~ ~ ~o. ~o ~,~ .~.~0 ......... ~,~ ..~.~ ......... m u~ ..~ ........
Rev. <~/30/aO
12/22/2011 13:53 631765~ OORCORAH NF PAGE 81/81
New York State Department of Environmental Conservation
Division of Environmental Permits, Region '1
SUNY @ Stony Brook
50 Circle Road, Stony Brook, NY 11790-3409
Phone: (631) 444-0365 · Fax: (631) 444-0360
LETTER OF NO JURISDICTION
TIDAL WETLANDS ACT
December 20, 2011
Joe Me,tens
Commissioner
430 WSD LLC
CIO Thomas Buchwalter
174 Mineola Bird
Ste. 201..
Mineola, N.Y. 11501
Dear Sirs:
Re:
UPA #1-4738-04082/00001
Facility: 430 West Shore Drive, Southold, N.Y.
SCTM #1000-80-5-2.1
Based ~)n the information you 'have submitted the Department of Enviro~mentai' Conservation
(DEC) has determined that;
The property landward of the bulkhead greater, than 1'00 feet in length .constructed .prior to
8/20177,. as evidenced on Aeroimage #72-2023 dated 4/6/76, and shown on the survey
prepared by Roderick Van Tuyl dated 11/29/95, is beyond Article 25 (Tidal Wel~and)
jurisdiction. Therefore, in accordance with the current Tidal Wetlands Land Use Regulations
(6NYCRR Part 661) no permit is required.
Be advised, no construction, sedimentation, or disturbance of any kind may take place
seaward of the tidal wetlands jurisdictional boundary, as indicated above, without a
permit. It is your responsibility to ensure that all precautions are taken to prevent any
sedimentation or other alteration or disturbance to the ground surface or vegetation within
Article 25 jurisdiction which may result from your project. Such precautions may include
maintaining adequate work area between the tidal wetland jurisdictional boundary and your
project (i.e. a 15' to 20' wide construction area) or erecting a temporary fence, barrier, or hale
bay berm.
Please no,t~¢~'thi~ letter does not relieve you of the responsibility of obtaining any necessary,
P~its ~~er agencies °r I°cal municipalities'
,.S, in~ere
· , .?..tr?Or. .. ., :.... .
cc: Nancy:C=e~'llS;: Fereshteh: Ghavimi, Hal:iita{-~i'Fil:~~ :':' ~''~:
1000-80-5-2.1
SHORE DRIVE, SOUTHOLD
SCTM: 1000-80-5-2,1
~HORE DRIVE,
SOUTHOLD BAY
~//
//
SCTM 1000-80-05-1.1
1700 ON( DRIV~
~U]HOLD, NY 11971
NOTES:
I. ELEVATIONS REFER TO ASSUMED DATUM
2. LOT AREA: 17,149 S.F. / 0.39 ACRES
3. PORTiONS OF ~ FRO~ SURVEY PREPARED
P~CONiC SURVEYORS, P.C,
1230 TRAV~J[R ~rREET, SOUTHOLD, NY 11971
SUR~'Y LAIEST DATED FEBRUARY 14. 2012
41"
41"
--4 ---
N 51'18'00" W 100.0
AUREL KARP,'~
MAR
Soutl
Board
WEST SHORE DRIVE
5 20]3
d Town
PROJECT LOCATION MAP
PROJECT
LOCATION
PROP[~5' OWNER:
Pt-1ER COSOLA
NOTES: 4557 DAVIS St[-FT
LONG ISLANO CflY. NY 11101
1. ELEVA11ONS REF[R TO ASSUMED DAIUM
2. LOT ARE~ 17,14g S,F. / 0.39 ACRES PREPARED BY:
5. PORtiONS OF FtAN FROt4 SURVEY PREPARED BY: JEFIEY PATANJO
106 HEY/fiT BOULEVARD
PECONIC SU~RVEIIORS, P.C. CENTER MORICHES, NY 11934
1230 ?RAVELER SLEET, SOUfl4OCD, NY I1971 651-484-9352
SURVEY LATEST DATED FEBRUARY 14. 2012
u ~ld-Town
Board
of
NYSDEPARTMENTOFENFIRONMENTA~5 CON$£RVATION 1/3,0/15
Pest management plays an integral role in the health and economic vitality of New York State.
At the same time, improperly used pesticides have the potential to impact environmental quality.
This draft Long Island Pesticide Pollution Prevention Strategy (Strategy) was developed in
response to concerns over detection of pesticide-related constituents in the groundwater over
time at various locations on Long Island and recognition of the importance of protecting the
environmental while meeting critical pest management needs.
The New York State Department of Environmental Conservation (DEC) regulates the
registration, commercial use, purchase and custom application of pesticides. The Environmental
Conservation Law (ECL) sets forth the state's policy regarding pesticide usage. ECL 33-0301.
According to the ECL, pesticides, when properly used, are "valuable, important and necessary to
the welfare, health, economic well-being and productive and industrial capabilities of the people
of this state." ECL 33-0301. However, pesticides also present potential dangers to health,
property and the environment if improperly used. ECL 33-0301.
DEC exercises its broad regulatory responsibilities in consultation with the Departments of
Health (DOH) and Agriculture and Markets (DAM) in order to protect public health and the
enxSronment while ensuring that pesticides proposed for use in New York State are properly
registered and applied for the benefit of agricultural and other economic enterprises that rely on
pesticide usage. In the interests of providing further protection to Long Island's precious
groundwater resources, DEC engaged the public, municipalities, agricultural and other regulated
communities in a discussion on how to further protect Long Island's groundwater resources. As
a result, DEC developed the draft Long Island Pesticide Pollution Prevention Strategy.
Implementation of the Strategy will enhance DEC's existing regulatOrY program using principles
ofpollutiun prevention. The Strategy presents a blueprint for DEC, in consultation with
stakeholders, to evaluate pesticide usage on Long Island, identify pesticides that have the
greatest potential to cause adverse impacts and work with partners to reduce or eliminate such
usage or find alternatives that do not present such impacts. This approach will both protect Long
Island's water resources from pesticide impacts and encourage effective methods of pest
management.
ES.1 THE CHALLENGE OF PESTICIDE USE AND GROUNDWATER ON LONG ISLAND
ES.1.A. Critical Natural Resource and Essential Pest Management
Almost three million people in Nassau and Suffolk Counties rely on clean drinking water from
Long Island's sole source aquifer, a unique and critical resource in the State. The heavy reliance
on the sole source aquifer plus the nature of the aquifer system itself(e.g., shallow depth of
groundwater, sandy and permeable soils overlying it), which is a factor in its vulnerability to
Executive Summary
Page ES- 1
contaminants, underscores the critical need to protect the quality of the groundwater before it
becomes impaired for such usage. Pesticides play an important and beneficial role in managing
pests on Long Island. This includes regional pests which threaten public health, agricultural and
horticultural productivity, structural integrity of public and private infrastructure (e.g.,
termite/carpenter ant control), quality of stored and marketed goods, and the condition of the
environment. Annual regional pesticide use by many entities (e.g., agriculture, businesses,
institutions and homeowners) averages in the millions of pounds and hundreds of thousands of
gallons.]
ES.1.B. Pesticide Detections in Long Island Groundwater
Water quality monitoring by Suffolk County and other entities shows that pesticides are among a
number of contaminants detected in Long Island groundwater as a result of a wide range of
human activities (e.g., nitrates, volatile organic compounds, pharmaceuticals and perSonal use
products). The water quality monitoring data presented in this document, as well as the water
quality monitoring data summary tables, are available at
ftp://ftp.dec.ny.gov/dshm/pesticid/liwaterqualitydata.docx Data obtained from Suffolk County
indicates that 117 pesticide-related chemicals were detected in the groundwater at a number of
locations on Long Island at various points in time since 1997. 2 Approximately half of these are
legacy compounds (from pesticides no longer or never registered for use on Long Island or in
New York State), which have not been used in many years. Although the samples demonstrate
that pesticides can persist in the Long Island aquifer, most detections were at low or trace levels.
Some pesticide-related compounds were detected (mostly at low levels) at multiple locations,
distributed broadly over Long Island. Primary examples include the active ingredients
imidacloprid (insecticide), metalaxyl (fungicide), and atrazine (herbicide)?
ES.1.C Drinking Water Quality
It is important to note that much of the water quality monitoring data presented in this document
does not represent what the majority of residents of Long Island are using for drinking and other
household purposes. Few detections of individual pesticide-related contaminants exceeded
applicable standards. The Suffolk County Water Authority finds that finished water (treated
water) that they supply to residents overall exceeds expectations for quality set by New York
State drinking water standards.4 Public water supplies are subject to regulation by the NYSDOH ·
through the Suffolk County Department of Health Services (SCDHS) under New York Codes
Rules and Regulation (NYCRR) Subpart 5-1.5 The regulations establish water quality standards
known as maximum contaminant Ievels (MCLs), and require routine water quality monitoring. If
finished drinking water is found to contravene a standard, corrective action is required. Private
wells are not regulated by NYSDOH, but SCDHS has a program to test private wells for
pesticides and other contaminants. Through their work, if contaminants are found in a private
1 NYS Department of Environmental Conservation, Final Annual Report for New York State Pesticide Sales and Applications
2005. htto://www.dec.nv.~ov/chemicaV37825.html
2 See Appendices A and B of the Strategy for a summary of results of Long Island water quality monitoring conducted by the
Suffolk County (SC) Deparlxnent of Health Services, SC Water Authority, and U.S. Geological Survey. See additional
monitoring data at htm://www.dec.nv.gov/.
3 DEC data analysis regarding these active ingredients (Als) is contained in Appendix B of this Strategy.
4 2012 Annual Drinking Water Quality Report, Suffolk County www.scwa.cora.
s Title 10. Department of Health Chapter I. State Sanitary Code Part5. Drinking Water Supplies Subpart 5-1. Public
Water Systems.
Executive Summary Page ES- 2
DRAFt LONG ISLAND PESTICIDE POLLUTION P~E, VENTION ST~TEGY
well that exceeds standards then the homeowner is advised to not drink that water, and to either
find an alternative source or to invest in treatment to achieve compliance with drinking water
standards.
ES.I.D. Significance of NYSDEC Pesticide Product Registration
DEC's pesticide product registration process forms an integral component of a comprehensive
pest management program. The product registration program acts as a gatekeeper to control thc
universe of pesticide products in New York State that may be made available consistent with
public health and environmental protection. The current in-depth pesticide product review
process did not exist prior to the early 1990s. Older pesticides, registered before that time, have
often not received a comprehensive DEC review, or received only a very limited review of a
subset of products. Thc data demonstrate that DEC's existing pest management regulatory
program has proven effective at preventing products which pose unreasonable adverse effects
from being registered and used in the State. DEC's enhanced pesticide registration program
relies on the New Active Ingredient (NAI) and Major Change in Labeling (MCL) review
process. During this process pesticide registrants work with DEC to implement a feasible and
effective resolution of any environmental concerns identified during DEC's review. For
example, some pesticides may be registered for usc in New York State with restrictions that
prohibit or modify use on Long Island if the chemical or product usc pattern poses a leaching
risk for Long Island's vuinemble gloundwater system. In this way, the current regulatory
process effectively provides pesticide products needed by the user community while ensuring
groundwater protection.
ES.2 PESTICIDE POLLUTION PREVENTION GOAL
In general, once a contaminant that has the potential to adversely impact public health or the
environment is found in groundwater, technological and fiscal constraints severely limit remedial
options, and accurate assessments of public health and environmental quality implications are
challenging. Therefore, it is essential to prevent contamination in the first instance, to the extent
practicable, while still allowing for needed pest management.
DEC developed this StrategY as an approach for managing the ongoing need tO prevent potential
pesticide impacts to water resources while continuing to meet critical pest management needs on
Long Island. In general terms, pollution prevention means reducing or eliminating the creation
of pollutants at the source. In the context of pesticides on Long Island, pollution prevention may
mean modifying pest management processes, promoting the use of alternative pest managemem
practices, and utilizing effective, less-toxic products when available.
GOAL OF
Prevent adverse effects on human health and the environment by protec~g
Long Island's groundwater and sur~tce water resources J~rom pesticide-related
to meet the pest management needs oJ: agricultural,
Industrial, and Institutional sectors.
Executive Summary Page ES- 3
ES.3 PESTICIDE POLLUTION PREVENTION (P2) BLUEPRINT
DEC's strategy to meet this goal of protecting water quality while meeting pest management
needs is based on a blueprint of actions to further pesticide pollution prevention on Long Island.
The greatest benefits can be gained from prevention when it is implemented through
collaboration with involved entities. Therefore, the pesticide pollution prevention (P2) blueprint
includes components to be acted on by DEC, in conjunction with various parmers and Long
Island stakeholders. In brief, the blueprint forms an approach for moving forward by
supplementing the existing protective measures of the product registration, compliance and
outreach components of DEC's pesticide regulatory program with P2 measures.
There are five main components in the pesticides P2 blueprint. The blueprint calls for actions
essential to effective implementation of pesticide P2 in Long Island and, without which the
Strategy cannot be meaningfully implemented. The blueprint is summarized below. Most of its
components are based on multi-party actions needed to bring pesticide P2 to fruition. The
actions must be feasible and carried out with available resources of DEC and its partners.
PESTI( IDE P2 BLUEPRINT SUMMARY
DEC Conducts Initial Assessments of Specific Active Ingredients (Als) and Related Pesticide
P2 Needs
DEC Forms, Convenes and Uhairs Pesticide P2 Workgroaps; Workgroups Consider Various
Matters Regarding Specified ,4is and Related P2 and Advise DEC
DEC Identifies and Prioritizes Pesticide P2 Measures and Partners Collaborate to Implement
P2 Measures
DE(' Tracks Pesticide P2 Results and Assesses Need for P2 Modifications
DEC Maximizes Department Use of Water Quality Monitoring for Pesticides (Monitoring
underlies implementation of the entire blueprln~)
These interrelated blueprint components tbllow a sequence which starts with assessing certain
pesticide active ingredients detected in Long Island groundwater, then evaluating the type of P2
needed and implementing it, followed by tracking P2 results and modifying P2 if needed.
Maximizing DEC use of water quality monitoring for pesticides involves actions which will
provide an important part of the foundation for implementing P2 throughout the blueprint.
A number of action steps are needed to implement each component of the blueprint. These are
shown in the full P2 blueprint on the following pages. Implementation of each component is
designed to yield benefits which facilitate car~ing out subsequent components and steps in the
P2 process. Further detail on the blueprint is contained in chapter 3.
Executive Summary Page ES- 4
BLUEPRINT £or~ONG 1,VLAND PESTICIDE POLLUTION PREVENTION
~NY~D.E.C Co~vt~ Initial Assessments of Active Ingredients (AIs) and Related
Review water quality monitoring results for Long Island groundwater; identify Als detected as
well as factors such as location, number, frequency and concentration of detections and potential
for human exposure and associated health risks.
} Review Al-related standards, use and product information and water quality standards and
benchmarks
~' Identify Als for which P2 measures potentially need to be taken
~, Identify types of additional information needed to consider potential pesticide P2 needs and
plan for Als.
Note: DEC anticipates that the first group of AIs to be considered for assessment will be
metalaxyl (fungicide), atrazine (herbicide) and imidacloprid (insecticide). These Als have been
detected by Suffolk County at multiple groundwater monitoring locations.
DEC Forms, Convenes and Chairs Pesticide P2 Workgroups; Workgroups Consider
Various Matters Re~ardin~ Als and P2
NYSDEC forms, convenes and chairs workgroups:
~' A Technical Review and Advisory Committee (TRAC) which, at the request of DEC,
considers AIs specified by the Depamnent and advises on factors such as AI use and
critical needs, potential for human exposure, human health risks, effective alternatives
for AI, aquifer vuinembility, potential pesticide P2 measures (see below), P2
implementation partners, and other considerations to provide DEC with background
information to support Department decisions regarding Als and related P2 actions and
implementation. (For further information on the TRAC, see Box ES-3 at close of the
Executive Summary.)
~. Additional workgroups, to ansure broad representation of involved entities in
consideration of Als and P2 measures (e.g., entities with direct involvement in pest
· management, pesticide Use, and water quality on Long Island as well as academia).
These workgroups may also consider Als specified by NYSDEC, provide NYSDEC
with requested information on particular subject areas (e.g., human health implications,
water quality concerns, effective alternatives), and suggest feasible P2 measures and
implementation partners.
NYSDEC Identifies and Prioriti[es Pesticide P2 Measures and Partners Collaborate to
Implement P2 Measures
NYSDEC considers workgroups' information and determines, thc scope and priority of pesticide
P2 measures appropriate for each Al to be addressed.
} NYSDEC will identify and prioritize P2 measures from among this overall scope of
primary P2 measures:
· Develop and disseminate best management practices and track their usc.
Executive Summary Page ES- S
DRAFTLONG ISLAND PESTICIDE POLLUTION PREVENTION STRATEGY
NYSDEPARTMENTOFENVIRONMENTAL CONSERVATION 1/30/13
BLUEPRINT for LONG ISLAND PESTICIDE POLLUTION PREVENTION
DEC Identifies and Prioriti~es Pesticide P2 Measures and Partners Collaborate to
Itnvlernettt P2 Meosures~ cont't~
· Research alternative products and practices, including organic practices, and provide
related outreach and education to implement
· Conduct outreach and education on use pattern-specific integrated pest management
· Encourage voluntary label revisions (through registrant and USEPA process)
· Restrict products to certified applicator use.
~' DEC will identify partners to collaborate with the Department to implement pesticide P2
measures (e.g., product registrants, user groups, academic entities~ State and local
agencies) and, as needed, convene P2 implementation workgroups.
~' DEC and partners will collaborate to implement P2 within available resources.
)~ DEC may strengthen existing outreach partnerships with Comell University and other
entities, forge new partnerships and maximize Interact resources.
)~ DEC and partners will identify stakeholders and build P2 implementation support.
DEC Tracks Pesticide P2 Results and Assesses Need for P2 Modifications or
Regulatory Measures
~. DEC, with, as needed, assistance of pesticide P2 partners, monitors results of P2
implementation and determines additional monitoring and measures, if any, for effective
pest management and water quality protection.
~ DEC may consider certain regulatory measures to manage use of a specific AI, if P2
actions prove insufficient and if DEC and NYSDOH determine that detections of a
pesticide-related chemical in water quality monitoring data indicate significant public
health or environmental impacts may occur. Under such circumstances, DEC may
reassess the registration status of products containing the target AI by reviewing the
product registrations associated With the AI and, if necessary, take regulatory action to
prohibit use on Long Island.
DEC Maximizes Department Use of Water OualitF Monitoring for Pesticides
NOTE: This underlies all actions under the blueprint, in that water quality monitoring results
are essential to conducting the work under each component (e.g., determining AIs to be
considered, specifying P2 needed, etc.)
~' Adjust emphasis of monitoring, as needed and within available resources and flexibility,
to meet DEC information needs for Long Island (e.g., focus on specific AIs to capture
information and discern trends and new detections in particular pesticide use settings,
such as greenhouses, turf, vineyards) as well as to monitor P2 results, if applicable.
~' Focus water quality monitoring, including the acquisition of finished drinking water
monitoring results, conducted under available resources by Suffolk County and Cornell
University or others, on AIs of concern to determine trends and changes in detection
levels and frequency.
Executive Summary Page ES- 6
DRAFT LONG ISLAND PESTICIDE POLLUTION PREVENTION STRATEGY
NYS DEPARTMENT OF ENVIRONMENTAL CONSERVATION 1/30/13
TECHNICAL REVIEW AND ADVISOR Y COMMITTEE (TRAC) -SUMMARYDESCRIPTION
Composition: DEC will convene, approximately six months after this Strategy is finalized, a
TRAC to pool expertise of State agencies and local government entities closely involved with
pesticide regulation and water quality monitoring for Long Island:
~ New York State: DEC (Chair), Department of Health, Department of Agriculture and
Markets
~ Local Entities: Suffolk County Department of Health Services, Water Authority, and Soil
and Water Conservation District; Nassau County Health Department; Cornell Cooperative
Extension of Suffolk County
After 5 years, Department and involved agencies assess ongoing need for TRAC.
Primary purposes:
~ Assist DEC in investigation and assessment of active ingredients (AIs), identified and
ranked by the Department (potential contaminants detected in Long Island groundwater)
> Consider factors such as groundwater monitoring data, exceedances of chemical-specific
water quality standards, potential for human exposure, public health risks, existing needs for
pest management, and pest management alternatives
~ Advise DEC regarding potential and feasible response actions to prevent further pesticide-
related impacts to the Long Island aquifer while recognizing pest management needs.
(Scope of response actions - see P2 measures in Information Box ES-I .)
For further information on the TRAC, see Chapter 3.
ES.4 SUMMARY OF LONG ISLAND PESTICIDE P2 STRATEGY CONTENTS
A summary of the contents of each chapter in the Strategy is contained in Table ES-1.
Executive Summary Page ES- 7
1/30/2013
Summary of Chapters and Appendices
I. Goal,
Philosophy,
~nd Purpose
?. Overview:
Groundwater
and Pesticide
Use on
Long Island
Goal: Given that groundwater, pest management and pesticide use are vital to public and economic welfare on Long Island, the overall goal
of this Strategy is to: ,
Prevent adverse effects to human health and the environment by protecting Long Island s groundwater and surface water resources from
pesticide-related contamination, while continuing to meet the pest management needs of agricultural, residential, commercial, industrial,
and institutional sectors.
Philosophy: The goal of entrancing water quality protection from pesticide impacts and maintaining needed pest management on Long
Island can be effectively achieved through a s~:ong pollution prevention approach that recognizes the importance of both and
mcorpomtes the involvement and cooperation of various stakeholders. Preventive measures can be taken to both minimize further
~esficide contamination after a pesticide has been detected and to prevent contamination before a pesticide is detected in water
resources.
Purpose: Establish a long-term pesticide pollution prevention blueprint to meet the goal of the Strategy and to outline enhanced DEC
>artuerships with involved entities that are essential to success. This blueprint should serve to enhance use of pest management methods on
Long Island that incorporate pollution prevention techniques and protect Long Island water resources from pesticide-related contamination.
Importance of Long Island sole source aquifer and its protection.
Aquifer structure and multiple uses by approx~ 3 million people make it a critical resource.
Pesticide-related statistics for Long Island:
· Of the 13,688 pesticides registered in the State, 361 are prohibited from use and 145 are registered for use on Long Island only when
certain conditions are met (June 2012);
· 4,733 cerdfied pesticide applicators and technicians on Long Island (2012);
· 5.3 million pounds and 407,000 gallons of pesticides applied on Long Island (2005).
Pesticide use yielded substantial benefits, including Suffolk County's statewide lead in sales of horticultural, agricultural and vineyard
products.
The signs of pestleide use are showing up in Long Island's groundwater. 117 pesticide-related chemicals detected in the aquifer at.
various locations since 1997; approximately half are legacy compounds (no longer or never registered in NYS). Some detections at
multiple locations and multiple compounds detected at individual wells.
Most pesticide-related detections are much lower than water quality criteria. Seven types of State and federal water quality criteria are
summarized.
Executive Summary
Page ES-8
1/30/2013
Chapter
3. Action Plan
to Implement
Pesticide
Pollution
Prevention
$trategy
~. Pesticide
Registration in
Yew York State
~. Existing
Pollution
Prevention
Programs and
Activities
Summary of Chapters and Appendices
Pollution prevention can prevent water quality impacts while continuing to meet critical pest management needs.
DEC Pesticide P2 Process Steps:
Conduct Initial P2 Needs Assessment
Determine Scope of Applicable P2 Measures
Convene P2 Working Groups
Review Information from P2 Working Groups as Basis for P2 Assessment
Identify and Prioritize Active Ingredients and P2 Measures
Convene and Collaborate with P2 Implementation Partners and Build Stakeholder Support
Conduct P2 Actions, Monitor Results of P2 Actions and Determine if Further/Modified Action Needed
History and evolution of New York State pesticide registration process
Current NYS registration process
NYSproduct revlew process for potential groundwater impacts - Safeguards against grotmdwater pollution built-into process
Factors considered during registration, include land and groundwater characteristics
Overview of leachate assessment and modeling of new active ingredients
Current Pesticide Use Statistics in NYS: Approximately 13,688 registered products, and 1,700 restricted pesticides, 361 of which are
prohibited from use on Lon~ Island
Summary of existing non-regulatory and regulatory measures to prevent or reduce potential impacts of pesticide use. Examples of
non-regulatory: outreach, education, best management practices, integrated pest management, environmental benefit projects,
agricultural environmental management. Examples of regulatory preventive measures: pesticide product registration, mixing and
loading requirements, toxic and hazardous materials storage, and local pesticide phase-outs.
Measures conducted by State and local governments, academia, pesticide users, interest groups and others.
6. Legal Summary of existing DEC statutory and regulatory authority over pesticides registration, sales, use, storage and disposal as well as
Authority and certain water quality requirements, primarily under the Environmental Conservation Law and related regulations.
Enforcement Comparison of DEC and USEPA authorities
Summary of DEC enforcement mechanisms related to pesticides
Summary of statutory authorities of other State agencies to conduct pesticide-related work, such as water quality and pesticide
management-related functions under the authority of State laws.
Appendices Appendix A Pesticide-Related Chemicals Detected In Long Island Groundwater 1996-2010
Appendix B DEC Summaries of Long Island Water Quality Monitoring Data
Appendix C TRAC Description and Ongoing Pest Management Education and Outreach Efforts
Executive Summary Page ES- 9
THIS PAGE INTENTIONALLY LEFT BLANK
~here is no known or expected health risk. MCLGs
allow for a margin of safety). These goals take into
account the risks of exposure for certain sensitive
populations, such as infants, the elderly, and persons
with compromised immune systems. These goals
are not enforceable levels because they do not take
available technology into consideration, and therefore
are sometimes set at levels which public water systems
cannot meet.
Propose an enforceable standard in the farm at a
Maximum Contaminant Level (MCL) (the maximum
amount of (J contarninant allowed in water delivered
lo a user of any public water system) or a Treatment
Technique (TT) (required procedure or level of
!ethnological performance sel widen ~here is no
~e[iable meihod to measure a con!aminant at very /ow
levels). MCLs are set as dose to MCLGs as feasible,
~onsidering available technology and cast. Examples
of rules requiring treatment techniques are the Surface
Wate~ T~eatment Rule (requires disinfection and
tlhration} and the Lead and Copper Rule (requires
~ptirnized corrosion control). Water samples that
~m~oin lead or copper exceeding the nction level
bigger additional treatment or other ~equirements
ti~a~ a water system must follow. Required testing
(monitoring) schedules are part of the enforceable
stcmdard.
After deterr'dning a proposed MCL or TT that is as
~lose to the MCLG as possible based on affordable
lechnology, US EPA must complete an economic
analysis o determine whether the benefits of that
s*andard justify the costs. If not, US EPA may adjust
ll~e MCL for a particular class or group of systems to
~ level that "maximizes health risk reduction benefits
u} a cost that is justified by the benefits." LIS EPA may
~ot adjust the MCL if the benefits justify the costs to
large systems and small systems that are unlikely to
t ecelve var[clnces
US EPA sets (m enforceable MCL or TT. After
cansiderh~g comments on the proposed standard and
other relevant information, US EPA makes final an
enforceable Max[inure Contaminan~ Level or Treatment
[ecimique, including required testing and reporting
~¢chedules
Candards fat systems serving up to 3,300 people
if the systems cannot afford to comply with a rule
or ~thet restructuring) and the systems install EPA
upproved variance technology. Slates can grant
wnlanees to systems serving 3,301 - 10,000 people
with US EPA approval SDWA does not ~dlaw small
Ihe exemntion period expires, the public wafer system
must be in compliance. The terms of variances and
h,~alli/
Determining Whether Sta.ndards Are
Needed for Other.Contaminants - the
Contaminant Candidate List
The 1996 Amendments to SDWA requires that every
5 years US EPA establish a list of contaminants which
a~e known or anticipated to occur in public water
systems and may require future regluations under
SDWA. The list is developed with significant input from
the scientific community and other interested parties.
After establishing this contaminant candidate list,
US EPA identifies contaminants which are priorities
for additional research and data gathering US EPA
uses this information to determine whether or not a
regulation is appropriate and this process is repeated
for each list, every 5 years.
In order t'o support this decision-making, US EPA
has also established a National Contaminant
Occurrence Database (NCOD), which stores data on
the occurrence of both regulated and unregulated
contaminants. US EPA is also required to list and
develop regulations for monitoring certain unregulated
contaminants. These monitoring data wJlJ provide the
basis for identifying contaminants that may be placed
on future Contaminant Candidate Lists and support
the US EPA Administrator's decisions to regulate
contaminants in the future.
Health Effects
Adverse health effects from contaminants that may
occur in drinking water include acute effects that may
immediately impact health and chronic effects that
may occur if contaminants are ingested at unsafe
levels over many years.
Drinking water that meets US EPA's health-based
standards is generally s'afe. People who are not
healthy as a result of Hiness, age, or weakened
immune systems, are more likely to be at risk from
certain contaminants that may be found in drinking
water, infants and very young children are also
more susceptible to some contaminants. Individuals
concerned about their particular situations should
consult their health care providers.
For More Information
To learn more about dcurrent drinking water
standards, information on potential health effects of
specific contaminants, and guidance fo persons with
severely compromised immune systems call tbe Safe
Drinking Water Hotline at 1-800 426~4791 or visit the
safewate(web site at wwwepa.gov/safewater.
Office of Water (4606) w,~,v, epa.gov/safewater EPA 816-F-04-037 June 2004
mm Drinking Water Standards
& Health Effects
SAFE DRINKING WATER ACT · 1974-2004 · PROTECT OUR HEALTH FROM SOURCE TO TAP
Drinking water standards are set by the .U.S.
Environmental Protection Agency (US EPA) to control
the level of contamir~c!nts in the nation's drinking
water. The Safe
Drinking Water Act
(SDWA) requires US EPA
to set these standards,
which public water
systems in the U.S~ are
required to meet. US
EPA has set standards
for 90 chemical,
microbiological,
radiological, and
physical contaminants
in drinking water. US
EPA and others are
currently conducting ~
research and
collecting information
to determine which
currently unregulated
contaminants pose the
greatest public health
risk and wilt therefore
be regulated in the
futSre.
US EPA also sets
Secondary Drinking
Water Regulations,
which are non-
enforceable guidelines
for contarninants that
may cause cosmetic
effects (such c~s skin
and tooth discoloration)
or aesthetic effects
(such as taste or odor).
Water systems are not required by US EPA to adopt
these secondary standards, but states may choose to
adopt and enforce them.
Pub. lie Watey Sy. stcms Must Meet
National Drank~ug Water Standards
Drinking water standards apply to public water
systems, which provide water to at least 15
connections or 25 persons at least 60 days out of
the year (most cities and towns, schools, businesses,
campgrounds, and shopping malls are served by
public water systems).
Private Wells
The 10 percent of Americans
whose water comes from private
wells (individual wells serving
fewer than 25 persons) are not
required to be protected by these
federal standards. People with
private wells are responsible
for making sure that their own
drinkiag water is safe. Some
states dO set standards for private
wells, so well owners should
check their state, requirements.
US EPA r¢cornmends testing
your water on~e per year to
see if it meet~ federal and state
standards. Civil the Safe Drinking
Water Hotline at 1-800-426-
4791 or see the Safewater home
page at www. epa.gov/safewater/
privatewells to find out how to get
a list of certified testing labs in
your state.
Bottled Water
Bottled water is regulated
by the U.S. Food and Drug
Administration as a food product,
and is required to rr;eet standards
equivalent to those US EPA sets
for tap water.
Steps in Drink. lng 'VVater
· Standard Settang:
US ~PA uses the following steps
to set enforceable, health-based drinking water
standards.
Determine whether a contaminant should be regulated
based on peer-reviewed science, including data on:
how often the contaminant occurs in the environment;
how humans are exposed to it; the health effects of
exposure, (particularly to vulnerable subpopulatjons).
Set a Maximum Contaminant Level Goal (MCLG) (the
level of a contaminant in drinking water below which
Federal Drinking Water Standards
Federal drinking water standards are in force for public water systems. Private water supplies are not subject to these
standards.
Public Water Systems
The term "public water system" means a system for the provision to the public of water for human consumption through
pipes or other constructed conveyances, if such system has at least fifteen service connections or regularly serves at
least twenty-five individuals.
The federal government has established regulatory limits (standards) on over 100 chemical and microbial contaminants in
drinking water. These have their origin in the Safe Drinking Water Act (SDWA), which governs public water systems.
Many states have established their own standards, which must be at least as stringent as the federal standards.
The U.S. Environmental Protection Agency (EPA) sets two types of standards:
Primary standards are set to provide the maximum feasible protection to public health. They regulate contaminant levels
based on toxicity and adverse health effects. The goal of standard setting is to identify maximum contaminant levels
(MCLs) which prevent adverse health effects.
Secondary standards regulate contaminant levels based on aesthetics such as color and odor, which do not pose a risk
to health. These secondary maximum contaminant levels (SMCLs) are guidelines, not enforceable limits. They identify
acceptable concentrations of contaminants which cause unpleasant tastes, odors, or colors in the water. SMCLs are for
contaminants that will not cause adverse health effects.
Public water suppliers are required to monitor the quality of the water they supply. Consumers mLIst be notified if a
primary standard is exceeded,
Health Advisories are guidance values based on non-cancer health effects for different durations of exposure (e.g., one-
day, ten-day, longer-term, and lifetime). They provide technical guidance to EPA Regional Offices, State governments,
and other public health officials on health effects, analytical methodologies, and treatment technologies associated with
drinking water contamination.
EPA maintains Webpage tables of the Primary and Secondary standards and Health Advisory guidance values. There are
consumer fact sheets on each of the contaminants for which there are primary standards.
Private Water Supplies
Users of private wells or other private water sources are solely responsible for monitorin,q and maintainin,q the quality of
their water supply. Some state or local health authorities regulate private water sources. Check with your local health
department.
Information Source: http://extoxnet.orst.edu/faqs/safedrinldstan.htm
MCLs and MCLGs
Establishing the Maximum Contaminant Level
The Maximum Contaminant Level (MCL) is the maximum concentration of a chemical that is allowed in public drinking
water systems. The MCL is established by the U.S. Environmental Protection Agency (EPA). Currently there are fewer
than 100 chemicals for which an MCL has been established; however, these represent chemicals that are thought to pose
the most serious risk.
The EPA guidance for establishing an MCL states that "MCLs are enforceable standards and are to be set as close to the
maximum contaminant level goals (MCLGs) (Health Goals) as is feasible and are based upon treatment technologies,
costs (affordability) and other feasibility factors, sueh as availability of analytical methods, treatment technology and costs
for achieving various levels of removal." The process of determining an MOL starts with an evaluation of the adverse
effects caused by the chemical in question and the doses needed to cause such effects. The final result of this process is
a safe dose (the dose thought to provide protection against adverse effects including a margin of safety), now called a
Reference Dose (RfD) by the EPA. This evaluation is based on the results of animal experiments, and the research
results are extrapolated to humans using standard EPA methods.
For chemicals that do not cause cancer, an MCLG is established by first converting the safe dose (RfD) to a water
concentration. Then this number is divided by five based on the assumption that exposure to the chemical through
drinking water represents only one-fifth of the possible exposure to this substance. Other sources of exposure may be air,
soil, and food. In almost all cases, the MCLG value is the same one that is used as the MCL.
For chemicals believed to cause cancer, (known or probable humans carcinogens - EPA Class A or B), the MCLG is set
at zero; i.e., no amount of chemical is considered acceptable. However, since zero cannot be measured, the MCL is
based on the lowest concentration that can be measured on a routine basis. This is known as the Practical Quantitation
Limit (PQL). Thus for known or probable carcinogens, the MCL is not a safe level but instead is the lowest measurable
level.
For chemicals that are possible cancer-causing agents (EPA Class C); i.e., there is some evidence that they may cause
cancer but this is not very convincing, a value equivalent to the MCLG is calculated as if they were not carcinogens. Then
this value is divided by a factor of ten to give the final MCLG..This provides an additional margin of safety in case the
chemical is later determined to be a carcinogen.'
A sample MCL calculation can be seen here.
What is equ va ent da y human intake for an average human?
Intake = RfD x body weight = 1 x 70 = 70 mg/day (Assume RfD = 1 mg/kg/day)
What concentration in drinking water would provide this intake?
Water concentration = intake/water consumption
= 70 mg/day divided by 2 liter/day = 35 rog/liter
But water consumption is assumed to be only 20% of total consumption,
MCL = 35 rog/liter x 0.2 = 7 rog/liter
If chemical is Class C carcinogen, divide by ten, so in this case:
MCL = 7/10 = 0.7 mg/liter
If chemical is Class A or B carcinogen, then:
MCL = Practical Quantitation Limit
Information Source: http:llextoxnet.orst.edulfaqslsafedrinklmcl.htm