Imperial wetland
THE NEW RIVER WETLANDS PROJECT IMPERIAL, CALIFORNIA
International Boundary and Water Commission (IBWC)
WHY IS IT INNOVATIVE?
The New River Wetlands Project is innovative because it uses constructed
wetlands in the desert to treat polluted surface water. Although wetlands have
traditionally been nature's filters, over 90% of natural wetlands have been lost in
California, leading to loss of habitat and degradation of water quality. While wetlands
have been constructed in the border region with the intent of restoring habitat, the use of
constructed wetlands for the main purpose of improving water quality is less common.
Typically, wetlands constructed to improve water quality have wastewater as their
source. A unique feature of the New River Wetlands Project is the use of surface water,
which requires sediment removal as a key aspect of treatment. While research has
documented the effectiveness of wetlands in improving water quality in other parts of
North America, the Salton Sea region has a unique climate, with extreme heat (an annual
average daily maximum temperature of 88 degrees) and little precipitation (less than
three inches per year). Localized testing was needed to evaluate the use of wetlands to
improve water quality in this region. Other important aspects of the project are creation
of habitat for fish and birds, and educational outreach that has involved hundreds
of
students in classroom activities, field trips, and work days.
ORGANIZATIONS INVOLVED
In early 1997, Desert Wildlife Unlimited, a local organization, looked for a
solution to the pollution problem. This group worked with local, state, and federal
agencies to obtain grant funds. Under the auspices of Desert Wildlife Unlimited, the
Citizen's Congressional Task Force on the New River was formed to develop the project.
The project has been implemented with participation from a variety of entities, including
Citizen's Congressional Task Force on the New River
Desert Wildlife Unlimited
Imperial Irrigation District
Bureau of Reclamation
County of Imperial
California Regional Water Quality Control Board
California Department of Fish and Game
U.S. Fish and Wildlife Service
U.S. Geological Survey
U.S. Environmental Protection Agency
Salton Sea Authority
PROBLEM STATEMENT
Water quality is impaired by the presence of high levels of suspended sediments,
nutrients (nitrogen and phosphorus), selenium, and coliform bacteria. Sediments,
suspended solids, and turbidity of the New and Alamo Rivers exceed objectives
established by the state Regional Water Quality Control Board, Colorado River Basin
Region. The New and Alamo Rivers acquire these pollutants from agricultural drainage
and urban sewage, especially sewage from Mexico. The concern is that pollutants carried
by the New and Alamo Rivers are degrading the Salton Sea, a saline lake in the Sonoran
desert located 40 miles north of the international boundary. These two rivers account for
80% of the flow into the Salton Sea.
The Salton Sea is a vital link for migratory birds on the Pacific Flyway and is
considered the nation's most productive fishery. Yet the Salton Sea's survival is at risk
due to increasing salinity, pollution, and decreased inflow. Excessive nutrients, including
phosphates and nitrates from runoff of agricultural fertilizers and municipal wastewater
contribute to eutrophication of the Salton Sea, which has no outlets. Controlling these
pollutants is one way to help preserve and restore the Sea.
APPROACH
Two pilot wetlands were constructed in 2000 to improve water quality in the New
and Alamo Rivers. Monitoring of these two sites has been conducted since 2001.
The Imperial Wetland, located approximately 13 miles north of the international
boundary near Imperial, California, has 22.7 wet acres. The source water is entirely
agricultural drainage from the Rice 3 Drain. The site has two sedimentation basins and
four wetland cells in series, a capacity of 127 acre-feet, a flow rate of 6 cubic feet per
second (cfs), and retention time of 9 days.
The Brawley Wetland, near Brawley California, approximately 20 miles north of
the border, has 6 wet acres with a capacity of 21 acre-feet. It treats water from the New
River. The wetland has one sedimentation basin and two wetland cells in series with a
flow rate of 1 cubic foot per second (cfs) and retention time of 7 days.
Flowing water enters the wetland where it settles into bottom sediments or is
subject to microbially-mediated reactions that may transform contaminants into volatile
or bioavailable forms or is incorporated into algae and plants. When eaten by fish and
invertebrates, it goes up the food chain. But eventually, these plants and animals die,
settling into the sediment. Over the long term, with sediment build-up, there is a
permanent sequestration of pollutants in the sediment.
Monitoring has been done for several years for the following parameters at
wetland inlets and outlets: - water temperature,
- dissolved oxygen,
- specific conductance,
- pH,
- barometric pressure,
- dissolved and total concentrations of organic carbon,
- total
phosphorus,
- nitrogen species (nitrate, nitrite, ammonia, total Kjeldahl nitrogen, and total
nitrogen),
- total suspended solids,
- dissolved selenium,
- bacteria (total and fecal coliforms,
and E. coli),
- biological oxygen demand,
- calcium,
- magnesium,
- sodium,
- potassium,
- total
alkalinity,
- hydroxide,
- carbonate,
- bicarbonate,
- sulfate,
- chloride,
- fluoride,
- total silica, and
- perchlorate.
Monitoring and analysis were done to characterize the removal of pollutants
from the two pilot wetlands to assist in developing designs for other wetlands in the
region.
The long-term goal of the project is to develop sufficient wetlands along the New
and Alamo Rivers to decrease the amount of total suspended solids, nitrogen,
phosphorous, and fecal coliforms, and to increase the amount of dissolved oxygen in these streams,
therefore benefitting the Salton Sea.
WHAT MAKES IT UNIQUELY A BORDER CASE?
The New River originates in Mexico, flows through Mexicali, Mexico into
Calexico, California and through Imperial County before emptying into the Salton Sea.
The New River at the international border is considered one of the most polluted streams
in the United States due to sewage arriving from Mexico. The river carries urban runoff,
agricultural runoff, and domestic and industrial waste from both countries. According to
the Regional Water Quality Control Board, New River flow at the border is about 150-
200 cfs, increasing to 600 cfs where it enters the Salton Sea.
The Alamo River also originates in Mexico about 2 miles south of the border. It
is dominated by agricultural return flows from the Imperial Valley. The Regional Water
Quality Control Board calculates flow at the border at 3-5 cfs, increasing to up to 1000
cfs at the Salton Sea delta.
The Salton Sea has important ecological connections with the Colorado River
Delta in Mexico. Both are key stops on the Pacific Flyway, linked by the riparian
corridors along the Colorado, Hardy, New, and Alamo Rivers. Over 400 bird species are
found in this region.
The New River Wetland Project is unique to the border region because it treats
water pollution arriving from Mexico and is part of a binational ecosystem.
RESULTS
Both the Brawley and Imperial Wetlands significantly reduced the amount of
nitrogen, phosphorous, pathogens (bacteria), and total suspended solids (sediment) in
water. Both wetlands removed over 90% of suspended sediments and pathogens
(measured as fecal coliform). Over 100 bird species have been found at the wetlands.
MEASUREABLE REDUCTION IN POLLUTION
Water quality monitoring conducted from 2001-2007 is summarized in the tables
below:
Imperial Site Water Quality Monitoring Summary (Averages)
|
January 2001 - April 2007
| Inlet | Outlet | %Change | Qualitative
DO
| 8.2
| 6.87
| 16.2
| decrease
Total N (mg/L)
| 6.8
| 3.5
| 48.5 | decrease
Total P (mg/L)
| 1.39
| 0.86
| 38.1 | decrease
Selenium (ug/L)
| 7.9
| 6.2
| 21.5 | decrease
BOD (mg/L)
| 12.0
| 11.2
| 6.7 | decrease
Fecal Coliform (MPN/100 ml) | 91,441 | 518
| 99.4 | decrease
TSS (mg/L)
| 192
| 11
| 94.3 | decrease
| | | | | | | |
Brawley Site Water Quality Monitoring Summary (Averages)
| January 2001 - April 2007
| Inlet |
Outlet | %Change | Qualitative
DO
| 3.43
| 7.73
| 125 | increase
Total N (mg/L)
| 7.9
| 2.2
| 72.2 | decrease
Total P (mg/L)
| 1.45
| 0.74
| 49.0 | decrease
Selenium (ug/L)
| 10.3
| 10.2
| 1.0 | decrease
BOD (mg/L)
| 11.6
| 10.8
| 6.9 | decrease
Fecal Coliform (MPN/100 ml) | 1.3 million | 547
| 99.9 | decrease
TSS (mg/L)
| 185
| 14
| 92.4 | decrease
| | | | | | | |
BENEFITS/SUCCESSES
The constructed wetlands provide the following benefits:
- Biologically and physically effective reduction of pollutants
- Outreach education available to all students in Imperial County
- Habitat for fish, migrating waterfowl, and a variety of other birds
- Recreational benefits such as hunting, fishing, bird watching, hiking, family outings.
FAILURES
Some bioaccumulation of selenium in invertebrates, fish, and bird eggs was
detected. Organochlorine pesticides were detected in tissue samples from fish and
invertebrates. There is a need to further study the risk associated with bioaccumulation of
toxics on wetland species. Over time, the rate of removal of phosphorus decreased. It is
unclear if this was due to year-to-year variations in loadings or other factors. This should
be monitored over the long term. Attempts to increase flow through the Imperial site
beyond the design flow caused the wetland cell levees to be overtopped. The wetlands
could not process the water fast enough to handle the increased flow.
UNINTENDED CONSEQUENCES
There are concerns about water contamination from bird feces and muskrats
eating bullrushes. Although the wetlands were intended to attract wildlife, negative
impacts of wildlife on the wetlands themselves are an unintended consequence.
LESSONS LEARNED
Differences in performance of the Brawley and Imperial sites provide guidance
for the design of future wetlands in the region. These differences relate to the
effectiveness of treatment and operation and maintenance issues. Pumps rather than
gravity were used at the Brawley site; due to the extra operation and maintenance
associated with pumping, designs and sites with gravity flow are preferred.
There is a need for further research as to why there is increased selenium retention
at the Imperial site as opposed to the Brawley site. The reasons for this are unclear.
The effects of infiltration into groundwater at the wetland sites are not
understood. Groundwater concentration data is needed to help understand these effects.
NATIONAL IMPLICATIONS
The New River Wetlands Project has demonstrated that wetlands with
sedimentation basins can provide highly-effective reduction of total suspended solids.
This suggests that wetlands can be used effectively to treat sediment-laden streams.
SOURCES
New River Wetlands Project brochure and website, www.newriverwetlands.com
Performance Evaluation of the New River Demonstration Wetlands, March 24, 2006.
Prepared for Citizen's Congressional Task Force on New River. Prepared by Tetra Tech,
Inc. in association with Wetlands Management Services. Available at:
www.newriverwetlands.com
Colorado River Basin Regional Water Quality Control Board,
http://www.swrcb.ca.gov/rwqcb7/water_issues/programs/salton_sea/index.shtml
Salton Sea Authority, http://www.saltonsea.ca.gov/
Brawley wetland
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