| Introduction | Methods and Materials | Data and Results | Discussion |
| Conclusion | Bibliography | Links | Photos |
Results
Chemical
Tests
Nitrate
levels in both site 1 and 2 were low, leveling off at .1 to .2 mg/L. throughout
our collections, except March 14 because the level jumped to 4.3 mg/L.
On March 14, 2001 the graph indicates 0 nitrate for site 1. The 0
stands for the data that was lost from that collection.
Turbidity
levels stayed constant, until the spring months because the water levels
rose. Again, data was lost on March 14, 2001 so the graph shows a
turbidity level of 0.
Phosphate
readings indicated a signifigant difference between site1 and site 2 on
the day of January 17, 2001. Site 1 reading values in at 0.1 mg/L;
however, site 2’s readings came in at 0.4 mg/L. Besides that date,
the levels stayed above the maxium limit of 0.1 mg/L.
D.O.
levels stayed constant and there was little change between the two sites.
The D.O. did drop slightly as the water warmed up.
Temperature
readings of the stream at site 1 varied normally. Temperature began
to rise in the water as the air temperature increased. We removed
hobos from their positions on April 20, 2001; therefore, data after April
20 is not valid.
Fish Collections
Thoughout
the winter and spring we baited minnows into 2 minnow traps set one mile
apart on the Beaver Creek Watershed. We caught 167 total fish during
this time. The species found were the Brook Stickleback, Cental Mudminnow,
Northern Redbellied Dace, Creek Chub, Blacknosed Dace, Golden Shiner, Rainbow
Trout, and unknown species. Brook Stickleback comprised 45% of the
collected fish; Central Mudminnow, 19%; Northern Redbellied Dace 19%; Creek
Chub 10%; Blacknosed Dace, 1%; Golden Shiner, .6%; Rainbow Trout, .6%;
and unknowns, 5%.
Results
| Ball Stream Habitat rating form | |
| FBI interpretation sheet | Chemical Data |
| FBI Results |