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Executive Summary xiii
Executive Summary
North Carolina’s Basinwide Approach to Water Quality Management
Basinwide water quality planning is a nonregulatory watershed-based approach to restoring and
protecting the quality of North Carolina’s surface waters. Basinwide water quality plans are
prepared by the NC Division of Water Quality (DWQ) for each of the 17 major river basins in
the state. Each basinwide plan is revised at five-year intervals. While these plans are prepared
by the DWQ, their implementation and the protection of water quality entail the coordinated
efforts of many agencies, local governments and stakeholders in the state. The first basinwide
plan for the Lumber River basin was completed in 1994 and the second in 1999.
This document is the third five-year update of the Lumber River Basinwide Water Quality Plan.
The format of this plan was revised in response to comments received during the first and second
planning cycles. DWQ replaced much of the general information in the first plan with more
detailed information specific to the Lumber River basin. A greater emphasis was placed on
identifying causes and sources of pollution for individual streams in order to facilitate local
restoration efforts.
DWQ considered comments from two public workshops held in the basin and subsequent
discussions with local resource agency staff and citizens during draft plan development. This
input will help guide continuing DWQ activities in the basin.
Goals of the Basinwide Approach
The goals of basinwide planning are to:
Identify water quality problems and restore full use to Impaired waters.
Identify and protect high value resource waters.
Protect unimpaired waters yet allow for reasonable economic growth.
DWQ accomplishes these goals through the following objectives:
Collaborate with other agencies to develop appropriate management strategies.
Assure equitable distribution of waste assimilative capacity.
Better evaluate cumulative effects of pollution.
Improve public awareness and involvement.
Lumber River Basin Overview
The Lumber River basin lies along the North Carolina/South Carolina border at the southeast
corner of the state, extending approximately 150 miles from the Sandhills region in southern
Moore and Montgomery counties to the Atlantic Ocean coastline in Brunswick County. Streams
and rivers in the Lumber River basin (except for the Lockwoods Folly and Shallotte Rivers) flow
into South Carolina and are tributaries of the Pee Dee River. Ultimately, the Pee Dee River
empties at Winyah Bay near Georgetown and Myrtle Beach, South Carolina.
Executive Summary xiv
From 1982 to 1997, urban and built-up land cover increased by 67,000 acres. Uncultivated
cropland decreased by 4,000 acres while pastureland remained about the same. Forest and
cultivated cropland cover significantly decreased by 30,000 and 41,000 acres, respectively. Most
land cover change is accounted for in the Lumber River basin hydrologic units that include
rapidly growing areas in Brunswick, Hoke, Moore and Robeson counties.
The Lumber River basin encompasses all or portions of nine counties and 51 municipalities. The
overall population of the basin based on the percent of the counties that are partially or entirely in
the basin is 304,579, with approximately 92 persons/square mile. The watersheds with an
increase in population are near Pinehurst, Laurinburg, Boiling Spring Lakes and Oak Island.
Populations of counties that are wholly or partly contained within the basin increased by over
501,308 people between 1990 and 2000. Hoke, Moore and Robeson counties are growing the
fastest in the upper basin, with Brunswick County growing the fastest in the lower basin. The
county populations are expected to grow by more than 156,000 by 2020. With the increased
population there will be increased drinking water demands and wastewater discharges. There
will also be loss of natural areas and increases in impervious surfaces associated with
construction of new homes and businesses.
There are 2,232.5 freshwater stream miles, 8,965.9 acres of freshwater, 4,306.6 estuarine acres,
and 25.6 miles of Atlantic coastline in the Lumber River basin. There are also countless miles of
unmapped small perennial, intermittent and ephemeral streams. The lower Lumber River basin
contains extensive wetland communities also. The basin starts in the Sandhills physiographic
region with about two-thirds of the basin in the Coastal Plain.
Assessment of Water Quality in the Lumber River Basin
Surface waters are classified according to their best intended uses. Determining how well a
waterbody supports its uses (use support status) is an important method of interpreting water
quality data and assessing water quality.
Surface waters are rated Supporting and Impaired. These ratings refer to whether the classified
uses of the water (such as water supply, aquatic life and recreation) are being met. For example,
waters assessed for aquatic life (Class C for freshwater or SC for saltwater) are rated Supporting
if data used to determine use support meet certain criteria. However, if these criteria were not
met, then the waters would be rated as Impaired. Waters with inconclusive data are listed as Not
Rated. Waters lacking data are listed as No Data. More specific methods are presented in
Appendix III.
In previous use support assessments, surface waters were rated fully supporting (FS), partially
supporting (PS), not supporting (NS) and not rated (NR). FS was used to identify waters that
were meeting their designated uses. Impaired waters were rated PS and NS, depending on their
degree of degradation. NR was used to identify waters lacking data or having inconclusive data.
The 2002 Integrated Water Quality Monitoring and Assessment Report Guidance issued by the
EPA requested that states no longer subdivide the Impaired category. In agreement with this
guidance, North Carolina no longer subdivides the Impaired category and rates waters as
Supporting, Impaired, Not Rated or No Data.
Executive Summary xv
Use support methods have been developed to assess ecosystem health and human health risk
through the development of use support ratings for six categories: aquatic life, fish consumption,
shellfish harvesting, recreation, water supply and "other" uses. These categories are tied to the
uses associated with the primary classifications applied to NC rivers, streams and lakes. A single
water could have more than one use support rating corresponding to one or more of the six use
support categories. For many waters, a use support category will not be applicable (N/A) to the
use classification of that water (e.g., shellfish harvesting is only applied to Class SA waters). A
full description of the classifications is available in the DWQ document titled: Classifications
and Water Quality Standards Applicable to Surface Waters of North Carolina. For more
detailed information regarding use support methodology, refer to Appendix III.
Aquatic Life
The aquatic life use support category is applied to all waters in North Carolina. Therefore, this
category is applied to all 2,232.5 freshwater stream miles, 8,965.9 acres of freshwater, 4,306.6
estuarine acres, and 25.6 miles of Atlantic coastline in the Lumber River basin. Approximately
32 percent of stream miles (723.1 miles) were monitored. Approximately 99 percent of
freshwater acres (8,875.3) and 50 percent of estuarine acres (2,170.0 acres) were monitored.
There were no Impaired stream miles, freshwater acres or estuarine acres. Table 1 summarizes
aquatic life use support ratings for the entire basin.
Table 1 Aquatic Life Use Support Summary Information for Waters in the Lumber River
Basin (1996-2001)
Aquatic Life
Use Support Ratings
All
Waters
Percent of
All Waters
Monitored
Waters
Percent of
Monitored Waters
Supporting 451.9 miles
8,875.3 acres
2,170.0 Est. acres
20.2
99.0
50.4
447.6 miles
8,875.3 acres
2,170 Est. acres
61.9
100.0
100.0
Impaired 0 miles
0 acres
0 Est. acres
0
0
0
0 miles
0 acres
0 Est. acres
0
0
0
Not Rated 299.4 miles
0 acres
0 Est. acres
12.0
0
0
275.5 miles
0 acres
0 Est. acres
38.1
0
0
No Data** 1,481.2 miles
90.6 acres
2,136.5 Est. acres
68.0
1.0
49.6
N/A
N/A
N/A
N/A
N/A
N/A
TOTAL 2,232.5 miles
8,965.9 acres
4,306.6 Est. acres
723.1* miles
8,875.3* acres
2,170.0* Est. acres
Note: Est. acres indicate saltwater (estuarine) acres; all other acres are freshwater acres.
* 32.4 percent of all stream miles, 98.9 percent of all freshwater acres, and 50.4 estuarine acres were monitored.
** There are also 25.6 miles of Atlantic coastline with No Data, not added to total mileage.
Executive Summary xvi
Fish Consumption
Like the aquatic life use support category, the fish consumption category is also applied to all
waters in the state. Approximately 1 percent of stream miles (21.5 miles) and 100 percent of
Atlantic coastline miles (25.6 miles) in the Lumber River basin were monitored for the fish
consumption use support category during this basinwide cycle. Fish consumption use support
ratings are based on fish consumption advice or specific advisories issued by the NC Department
of Health and Human Services (NCDHHS). If a limited fish consumption advice, advisory or a
no consumption advisory is posted at the time of use support assessment, the water is rated
Impaired. A basinwide summary of current fish consumption use support ratings is presented in
Table 2.
Table 2 Fish Consumption Use Support Summary Information for Waters in the Lumber
River Basin (1996-2001)
Fish
Consumption
All
Waters
Monitored
Waters
Percent
Monitored
Supporting 0 miles
0 acres
0 Est. acres
0 miles
0 acres
0 Est. acres
0
0
0
Impaired 2,232.5 miles
8,965.9 acres
4,306.6 Est. acres
25.6 coast
21.5 miles
0 acres
0 Est. acres
25.6 coast
1
0
0
100
Not Rated 0 miles
0 acres
0 Est. acres
0 miles
0 acres
0 Est. acres
0
0
0
TOTAL 2,232.5 miles
8,965.9 acres
4,306.6 Est. acres
25.6 coast
21.5 miles
0 acres
0 Est. acres
25.6 coast
1
0
0
100
Note: Est. acres indicate saltwater (estuarine) acres; all other acres are freshwater acres.
Coast indicates miles of Atlantic coastline in the Lumber River basin.
Recreation
Like the aquatic life use support category, the recreation category is also applied to all waters in
the state. Approximately 12 percent of stream miles (262.2 miles) were monitored by DWQ.
There were no stream miles Impaired in the recreation use support category. Approximately 99
percent of freshwater acres and 47 percent of estuarine acres were monitored. Table 3
summarizes recreation use support ratings for the entire basin.
Executive Summary xvii
Table 3 Recreation Use Support Summary for Waters in the Lumber River Basin (1996-
2001)
Recreation All
Waters
Monitored
Waters
Percent of
Monitored Waters
Supporting 257.1 miles
8,840.2 acres
2,039.2 Est. acres
25.6 coast
257.1 miles
8,840.2 acres
2,039.2 Est. acres
25.6 coast
11.5
98.6
47.4
100
Impaired 0 miles
0 acres
0 Est. acres
0 miles
0 acres
0 Est. acres
0
0
0
Not Rated 5.1 miles
0 acres
0 Est. acres
0 coast
5.1 miles
0 acres
0 Est. acres
0 coast
0.2
0
0
0
No Data 1,970.3 miles
125.7 acres
2,276.3 Est. acres
N/A miles
N/A acres
N/A Est. acres
N/A
N/A
N/A
TOTAL 2,232.5 miles
8,965.9 acres
4,306.6 Est. acres
25.6 coast
262.2 miles
8,840.2 acres
2,039.2 Est. acres
25.6 coast
Note: Est. acres indicate saltwater (estuarine) acres; all other acres are freshwater acres.
Coast indicates miles of Atlantic coastline in the Lumber River basin.
Water Supply
There are 216.7 stream miles currently classified for water supply in the Lumber River basin. All
water supply waters are Supporting on an evaluated basis based on reports from DEH regional
water treatment consultants.
Shellfish Harvesting
There are 4,280.8 estuarine acres classified for shellfish harvesting (Class SA) in the Lumber
River basin. All were monitored during the past five years by DEH Shellfish Sanitation (refer to
page 45). Impaired estuarine acres accounted for 15.7 percent of the total estuarine acres in the
shellfish harvesting use support category. A basinwide summary of current shellfish harvest use
support ratings is presented in Table 4.
Executive Summary xviii
Table 4 Shellfish Harvesting Use Support Summary Information for Waters in the Lumber
River Basin
Shellfish
Harvesting
Monitored
Waters
Percent of
Monitored
Supporting 673.9 acres 100
Impaired 3,606.9 acres 100
Not Rated 0 acres 100
TOTAL 4,280.8 acres 100
Impaired Waters
Table 5 presents Impaired waters (in all categories) in the Lumber River basin that were
monitored by DWQ within the last five years. The use support category for which a waterbody
is Impaired is indicated in the table. Descriptions of Impaired segments, as well as problem
parameters, are outlined in Appendix III. Management strategies for each waterbody are
discussed in detail in the appropriate subbasin chapter. Maps showing current use support
ratings for waters in the Lumber River basin are presented in each subbasin chapter in Section B.
Table 5 Monitored Impaired Waters within the Lumber River Basin (as of 2003)
Waterbody Subbasin Chapter in
Section B Classification Miles Acres Use Support
Category
Lumber River * 03-07-51 2 C Sw 21.5 0.0 Fish Consumption
Intracoastal Waterway 03-07-59 10 SA 0.0 2,117.6 Shellfish Harvesting
Lockwoods Folly River 03-07-59 10 SA 0.0 606.2 Shellfish Harvesting
Mill Creek 03-07-59 10 SA 0.0 2.0 Shellfish Harvesting
Mullet Creek 03-07-59 10 SA 0.0 5.7 Shellfish Harvesting
Lockwoods Creek 03-07-59 10 SA 0.2 0.0 Shellfish Harvesting
Spring Creek 03-07-59 10 SA 0.0 2.4 Shellfish Harvesting
Shallotte River 03-07-59 10 SA 0.0 647.3 Shellfish Harvesting
The Mill Pond 03-07-59 10 SA 0.0 2.8 Shellfish Harvesting
Sams Branch 03-07-59 10 SA 0.6 0.0 Shellfish Harvesting
The Swash 03-07-59 10 SA 0.0 3.9 Shellfish Harvesting
Shallotte Creek 03-07-59 10 SA 0.0 135.6 Shellfish Harvesting
Saucepan Creek 03-07-59 10 SA 0.0 62.6 Shellfish Harvesting
Jinnys Branch 03-07-59 10 SA 0.0 1.0 Shellfish Harvesting
Goose Creek 03-07-59 10 SA 0.0 4.2 Shellfish Harvesting
Big Gut Slough 03-07-59 10 SA 0.0 0.3 Shellfish Harvesting
Kilbart Slough 03-07-59 10 SA 0.0 0.7 Shellfish Harvesting
Calabash River 03-07-59 10 SA 0.0 3.4 Shellfish Harvesting
Hangman Branch 03-07-59 10 SA 0.0 10.2 Shellfish Harvesting
Atlantic Coastline * 03-07-59 10 SB 25.6 0.0 Fish Consumption
* Although all waters in the basin are considered Impaired for the fish consumption use support category, only the Lumber River (21.5
miles) and the Atlantic coastline (25.6 miles) were monitored (see page 59).
Executive Summary xix
Recommended Management Strategies for Restoring Impaired Waters
The long-range mission of basinwide planning is to provide a means of addressing the complex
problem of planning for increased development and economic growth while maintaining,
protecting and enhancing water quality and intended uses of the Lumber River basin’s surface
waters. Within this basinwide plan, DWQ presents management strategies and recommendations
for those waters considered Impaired or that exhibit some notable water quality problem.
Major water quality problems in the basin include habitat degradation, algal blooms, low
dissolved oxygen (affecting aquatic life), mercury in fish tissue (affecting fish consumption), and
fecal coliform bacteria contamination (affecting shellfish harvesting). Habitat degradation,
including sedimentation, streambed scour and streambank erosion, is primarily attributed to
nonpoint source pollution (NPS). Sources of nonpoint source pollution include runoff from
construction sites, agricultural lands and urban areas, and hydromodification.
For streams degraded by point source pollution, the plan presents a management strategy to
reduce the impacts from that pollutant source. The task of quantifying nonpoint sources of
pollution and developing management strategies for these Impaired waters is very resource
intensive. This task is overwhelming, given the current limited resources of DWQ, other
agencies (e.g., Division of Land Resources, Division of Soil and Water Conservation,
Cooperative Extension Service, etc.) and local governments.
DWQ plans to further evaluate Impaired waters in the Lumber River basin in conjunction with
other agencies that deal with nonpoint source pollution issues and develop management
strategies for a portion of these Impaired waters for the next Lumber River Basinwide Water
Quality Plan (2008).
Addressing Waters on the State’s 303(d) List
Section 303(d) of the Clean Water Act requires states to identify waters not meeting standards.
EPA must then provide review and approval of the listed waters. A list of waters not meeting
standards is submitted to EPA biennially. Waters placed on this list, termed the 303(d) list,
require the establishment of total maximum daily loads (TMDLs) intended to guide the
restoration of water quality. EPA issued guidance in August 1997 that called for states to
develop schedules for developing TMDLs for all waters on the 303(d) list within 8-13 years.
The 303(d) list and accompanying data are updated as the basinwide plans are revised. In some
cases, the new data will demonstrate water quality improvement and waters may receive a better
use support rating. These waters may be removed from the 303(d) list when water quality
standards are attained. In other cases, the new data will show a stable or decreasing trend in
overall water quality resulting in the same, or lower, use support rating. Attention remains
focused on these waters until water quality standards are met. Currently, there are 11 waters
listed on the North Carolina’s 2002 Integrated 305(b) and 303(d) Report in the Lumber River
basin. These waters were listed for fish consumption advisories related to mercury. Several of
these waters have not been monitored by DWQ, but still are considered Impaired on an evaluated
basis due to the current fish consumption advice from the NC Department of Health and Human
Services.
Executive Summary xx
Challenges Related to Achieving Water Quality Improvements
To achieve the goal of restoring Impaired waters throughout the basin, DWQ will need to work
more closely with other state agencies and stakeholders to identify and control pollutants. The
costs of restoration will be high, but several programs exist to provide funding for restoration
efforts. These programs include the Clean Water Management Trust Fund, the NC Agricultural
Cost Share Program, the Wetlands Restoration Program and the federally funded Environmental
Quality Incentives Program.
With increased development occurring, there will be significant challenges ahead in balancing
economic growth with the protection of water quality in this basin. Point source impacts on
surface waters can be measured and addressed through the basinwide planning process.
Nonpoint sources of pollution can be identified through the basinwide plan, but actions to
address these impacts must be taken at the local level. Such actions should include:
development and enforcement of local erosion control ordinances; requirement of stormwater
best management practices for existing and new development; development and enforcement of
buffer ordinances; and land use planning that assesses impacts on natural resources. This
basinwide plan presents many water quality initiatives and accomplishments that are underway
within the basin. These actions provide a foundation on which future initiatives can be built.