Of Time and the River
The Period 1972 to Present
 

  Non-point Source Pollution (continued)

In 1986, the ISGS conducts an assessment of sedimentation rates and contamination levels from 18 sampling stations located in the backwater lakes. A total of 112 samples are tested. The surface area, shoreline length, maximum depth, and condition (Table 36) are assessed. In general, the lakes are in poor condition due to unstable water levels, high turbidity, and high sediment deposition (Cahill 1986).

Table 36: Physical parameters for backwater lakes sampled along the Illinois River (Cahill 1986)

 
  Surface area 
(acres)
Shoreline length 
(km)
Maximum depth 
(m)
Condition 
Silver Lake 40 4.5 1.5 Fair
Swan Lake 2345 25.9 1.5 Fair
Meredosia Lake 1692 29.0 1.5 Fair
Muscooten Bay 1646 13.0 1.8 Poor
Stewart Lake 1578 17.7 1.2 Poor
Matanzas Lake 861 11.3 2.4 Poor
Quiver Lake 407 3.9 1.2 Poor
Lake Chautauqua  3562 22.5 1.2 Poor
Clear Lake 1463 14.8 0.9 Poor
Goose Lake 2822 19.3 1.5 Poor
Sawmill Lake 630 11.3 - Poor
Senachwine Lake 3324 22.5 1.5 Poor
Depue Lake 524 11.3 1.8 Poor
Turner Lake 300 5.8 - Unknown

Source: 1978 Assessment and classification of Illinois Lakes, IEPA

Sedimentation rates as measured by Frank Bellrose in 1983 are found in Table 37, and the rates measured in 1984 M.T. Lee are in Table 38. The discrepancies between the two data sets are due in part to fluctuating water levels (Cahill 1986). Sedimentation rates range from 1.0 cm/year in Swan Lake to 3.2 cm/year in Depue Lake.

Table 37: Sedimentation Rates and Depth at Different Periods (Cahill 1986)

 
  Time Interval  Sedimentation Rate 
(cm/yr)
Sediment Depth 
(cm)
Senachwine Lake 1903-1978 1.27 95
Sawmill Lake 1903-1978 1.11 83
Goose Lake 1903-1978 1.07 80
Upper Peoria Lake  1903-1965 1.67 104
  1965-1976 3.06 34
  1903-1976 1.88 137
Clear Lake 1903-1978 1.56 117
Lake Chautauqua 1926-1950 1.05 25
  1950-1976 1.06 27
  1926-1976 1.05 52
Matanzas Lake 1903-1979 1.62 123
Meredosia Lake 1903-1956 1.30 69
  1956-1978 1.19 26
  1903-1978 1.27 95
Swan Lake 1903-1978 0.85 64

Source: Bellrose et al, 1983

Sediment accumulation is extreme in several lakes, such as Peoria Lake and Muscooten Bay. The sedimentation rate in Upper Peoria Lake is nearly two times greater during 1965-1976 than the long-term average of 1.67 cm/yr from 1903-1976. This increased rate over an 11-year period results in 34 cm of sediment being deposited - nearly one-quarter of the total amount of sediment deposited.

Table 38: Sedimentation rates in Illinois River backwater lakes (Cahill 1986)

 
Location  Sedimentation rate 
(cm/yr)
Swan Lake 0.46
Meredosia Lake 1.09
Muscatoon Bay 7.92
Lake Chautaqua 0.83
Peoria Lake 1.02
Sawmill Lake 1.02
Senachwine Lake  0.76
Depue Lake 1.50

Source: data for Table 38 taken from Lee, 1984

The combination of large surface areas and shallow depths alters these lakes from ones with high diversity of aquatic plants to “saucer-shaped basins filled with soft sediments that support little or no life” (Cahill 1986). These lakes are further degraded from wind- and barge-generated waves and recreational boating, which cause resuspension of bottom sediments. This resuspension degrades the lakes by:

Depue Lake is located in the Upper Illinois River, downstream of Spring Valley. It is connected to the Illinois River by a narrow channel. This lake was popular for boating before World War II when the depth was reported to be 18-20 feet. Sediment has since been carried in during flood stages of the river, resulting in a decrease in storage capacity of 72.6% between 1903 and 1975. The average water depth is now 1½ feet (0.5 m) (Cahill 1986).

Sediments are tested for concentrations of metals. Zinc (Zn), lead (Pb), and cadmium (Cd) concentrations are higher in upstream lakes as compared to downstream lakes. Zinc concentrations range from 5,000 ppm at Depue Lake to 132 ppm at Silver Lake