|
Attachment Two: Errata
The following corrections to the IPM Program and corresponding
EA are being made and incorporated herein by reference into the Agency
Record. A Final IPM Program will be printed which reflects these changes.
|
PGC IPM PROGRAM EDITS
|
| Section/paragraph |
Old Text |
Revised Text
(additions/changes highlighted)
|
| 2.5 paragraph 1 |
The Colma Foundation is a poorly undulated sandstone
that consists of flat lying fine-grained, silty sand, and occasional
beds of clay derived from ancient sand dunes and alluvial material
dating back to the Pleistocene in the last ice age (Schlocker, 1974) |
The Colma Foundation is a poorly indurated
sandstone that consists of flat lying fine-grained, silty sand, and
occasional beds of clay derived from ancient sand dunes and alluvial
material dating back to the Pleistocene in the last ice age (Schlocker,
1974) |
| 2.8.3 paragraph 2 |
A minor subbasin exists at the top of the course, which
drains in a southeasterly direction. |
A minor subbasin exists at the top of the course
(half of hole 18), which drains in a southeasterly direction
toward Tennessee Hollow. |
| 2.8.3 paragraph 3 |
The first subbasin drains holes 1, 2, 3, half of 8,
9, 10, and 18. |
The first subbasin drains holes 1, 2, 3, half of 8,
9, 10, and half of 18. |
| 2.8.3 paragraph 3 |
|
Added: The downstream end of this
canal is intended to be restored to native habitat by the Presidio
Trust, National Park Service, and Golden Gate National Parks Association,
under the Mountain Lake Enhancement Plan. |
| 2.8.3 paragraph 5 |
|
As suggested by the NPS, the text was changed to include
hole 5 in the second subbasin, and to clarify that the third subbasin
ultimately drains to Mountain Lake. |
3.2 paragraph 1
Turf Selection guidelines |
|
Added:
Invasiveness. Non-invasive turf grasses
should be selected to reduce the possibility of the spread of non-native
grasses throughout the Presidio. |
| Table 12.1 |
|
Section numbers referenced in the table have been updated
to reflect changes made since the previous draft in order to refer
to the correct sections of the program. |
| 12.6 paragraph 1 |
A RAVE score will be calculated on a case-by-case
basis for each pesticide application before it occurs, and no applications
that pose a moderate or high risk to groundwater (i.e. RAVE score
of 65 or greater) will occur on the course. |
The following typographical correction has been made:
A RAVE score will be calculated on a case-by-case basis for each
pesticide application before it occurs, and no applications that
pose a moderate or high risk to groundwater (i.e. RAVE score of
45 or greater) will occur on the course.
|
| 12.9 paragraph 1 |
|
Addition of the following sentence: If
an adjuvant would increase a pesticide's leachability, this must be
accounted for in the RAVE analysis (see Section 12.6) of the application. |
| 13.1.7 paragraph 1 |
Applications with a RAVE score of 65 or greater shall
not occur on the course. |
The following typographical correction has been made:
Applications with a RAVE score of 45
or greater shall not occur on the course. |
| 14.3 List of stormwater sampling locations |
|
Addition of a 7th stormwater sampling location:
In the rough to the northeast of the back half
of the 18th fairway. (This location point was also added
to figure 4) |
| Chapter 13 Title |
Chemical Pesticides |
Chemical Pesticides: Use and Restrictions |
| Chapter 14 Title |
Environmental Monitoring, Reporting, and Mitigation |
Water Quality Monitoring,
Reporting, and Mitigation |
| 14.1 |
Monitoring of surface and near surface groundwater will
be done to assess the movement, if any, of pesticides applied to the
course. |
Monitoring of surface water
and near surface groundwater will be done to assess the movement,
if any, of pesticides applied to the course. |
| 14.2 paragraph 1 |
After any pesticide application on fairways, piezometers
at the 1st, 12th, and 14th fairways will be monitored for flow and
sampled if water is available. |
After any pesticide application on fairways, piezometers
at the 1st, 12th, and 14th fairways will be monitored for the
presence of water and sampled if water is available. |
| 14.2 paragraph 2 |
Approximate flow rate in gallons per hour or equivolent
units will be recorded at the time of the sampling. |
Approximate flow rate through
the drain box in gallons per hour or equivolent units will
be recorded at the time of the sampling. |
| 14.3 paragraph 3 |
Samples will be analyzed for pH, total dissolved solids
(TDS), nitrate, ammonia, sulfate, phosphate, and the last pesticide
applied to the course. |
Samples will be analyzed for pH, total dissolved solids
(TDS), nitrate, ammonia, sulfate, phosphate, and any
pesticide applied to the course in the previous twelve months. |
| 14.5 |
If this assessment indicates that continued use of a
pesticide poses a risk, consultation with qualified personnel from
the Trust, and from one or more of the following organizations will
occur: DPR, the manufacturer, the Trust, or other qualified experts. |
If this assessment indicates that continued use of a
pesticide poses a risk, consultation with the Trust
IPM Coordinator, and from one or more of the following organizations
will occur: DPR, the manufacturer, University
Extension, or other qualified experts. |
14.5
Figure 60: Pesticide monitoring and use decision tree |
|
Changed the decision tree so that the "consultation
box" precedes the "Risk Present?" decision. |
|
PGC IPM PROGRAM ENVIRONMENTAL ASSESSMENT (EA)
|
| Section |
Old Text |
Revised Text (additional/changes highlighted) |
| E-9 |
However, no requirements for preventative
management or non-chemical pest management would be enforced. Consequently,
the use of chemical pest management could increase, and chemicals
with higher risk to groundwater could be called for. |
However, no requirements for preventative management
or non-chemical pest management would be enforced under
the No Action Alternative. Since it is the use of preventative management
and monitoring to catch pests early that allows for the effective
use of mant of the low-risk pesticides, pesticides with higher
risk to groundwater could be called for under
this alternative. |
| E-19&20 |
|
Added the following paragraph: Under
the No Action Alternative, pesticide storage and selection would be
conducted according to CA EPA guidelines. Thus, storage requirements
would be the same as the preferred alternative, but the selection
of pesticides could be of higher risk pesticides (see Section E-9).
All applicable laws and regulations for the storage and handling of
these materials would be implemented. |
| E-25 |
Expose pesticides to fish? |
Expose fish to pesticides? |
| E-31 |
These actions include projects implementing
the Presidio Vegetation Management Plan, the Mountain Lake Enhancement
Plan, the Draft Recovery Plan for Coastal Plants of the Northern San
Francisco Peninsula, the Crissy Field Plan, the Tennessee Hollow Restoration
Plan, and the Presidio Golf Course Habitat and Wildlife Management
Plan. |
These actions include projects implementing the Presidio
Vegetation Management Plan, the Mountain Lake Enhancement Plan, the
Draft Recovery Plan for Coastal Plants of the Northern San Francisco
Peninsula, the Crissy Field Plan, the Tennessee Hollow Restoration
Plan, and the Presidio Golf Course Habitat and Wildlife Management
Plan, and the Lobos Creek Water Quality Management
Plan. |
|