Maine Department of Environmental Protection
Biological
Monitoring Program
Stream Algae Report
| Name: | Stone Brook - Station 944 | Sampled by: | Biomonitoring Unit |
| Town: | Augusta | Method: | Rock Scrapings 1 Inch Circles |
| Biomonitoring Basin | Kennebec | Sample ID: | SA-944-2017R (1677) |
| Sample Date: | 2017-07-10 | Taxonomist: | Ecoanalysts Idaho |
| Location: | ~0.2 Miles Down Stony Brook Road. New Location - 41 Anthony Drive Park At Very Back Left End Of Health And Human Services. Hop Off End And Walk Down To Stream. Or Dhhs Parking Lot |
| Sample comments: | |
| Latitude: | 44.34513057 |
| Longitude: | -69.80070179 |
Blue = this sample. Boxplots = range of all samples. Grey shaded
areas = 90th and/or 10th percentile of reference site values.
| Statutory Class = B |
| Final Determination = C |
| Attains Class = NO |
| Reason = Model |
| Model Result = C |
| Prob. Class A = 0.00 |
| Prob. Class B = 0.00 |
| Prob. Class C = 0.96 |
| Prob. NA = 0.04 |
Blue = this sample. Boxplots = range of all samples. Grey shaded
areas = 90th and/or 10th percentile of reference site values.
| Variable | Sample value | All data median | All data 10th percentile | All data 90th percentile | Reference range lower limit | Reference range upper limit | Reference range description |
|---|---|---|---|---|---|---|---|
| Salt-tolerant diatom percent abundance | 6.73 | 0.90 | 0.00 | 9.15 | 0.00 | 1.08 | <90th percentile |
| Nutrient-tolerant diatom richness | 18.00 | 8.00 | 3.00 | 17.00 | 0.00 | 8.00 | <90th percentile |
| Intermediate diatom richness | 24.00 | 19.00 | 11.00 | 28.80 | 9.00 | 25.30 | 10th to 90th percentile |
| Intolerant algae percent species | 2.63 | 18.75 | 3.70 | 42.27 | 22.12 | 72.41 | >10th percentile |
| Motile diatom percent abundance | 16.32 | 8.49 | 1.55 | 31.56 | 0.00 | 11.59 | <90th percentile |
| Tolerant algae percent abundance | 14.90 | 1.19 | 0.00 | 17.43 | 0.00 | 1.05 | <90th percentile |
| Variable | Sample value | All data median | All data 10th percentile | All data 90th percentile | Reference range lower limit | Reference range upper limit | Reference range description |
|---|---|---|---|---|---|---|---|
| Tolerance Index (all algae) | 46.77 | 42.67 | 37.09 | 49.07 | 0.00 | 42.34 | <90th percentile |
| Nitrogen Index (all algae) | 50.93 | 38.64 | 26.81 | 51.56 | 0.00 | 35.58 | <90th percentile |
| Phosphorus Index (all algae) | 72.36 | 58.62 | 38.59 | 76.56 | 0.00 | 53.06 | <90th percentile |
| Intolerant algae percent species | 1.00 | 6.00 | 1.00 | 14.00 | 5.00 | 23.00 | >10th percentile |
| Intolerant algae richness | 9.09 | 6.25 | 0.00 | 16.00 | 0.00 | 7.14 | <90th percentile |
| Salt-tolerant diatom percent richness | 83.12 | 89.95 | 61.14 | 98.30 | 45.42 | 97.96 | 10th to 90th percentile |
| Tolerant algae percent richness | 34.21 | 16.67 | 0.00 | 41.38 | 0.00 | 14.29 | <90th percentile |
| Nutrient- tolerant diatom percent abundance | 37.16 | 42.06 | 7.59 | 84.31 | 0.00 | 48.33 | <90th percentile |
Blue = this sample. Boxplots = range of all samples. Grey shaded
areas = 10th to 90th percentile of reference site values
| Bankfull width = 10 m |
| Wetted width = 6 m |
| Depth = 12 cm |
| Water velocity = 30 cm/s |
| Riffle = 40 % |
| Run = 40 % |
| Pool = 20 % |
| Canopy Cover = 78 % |
| Boulder = 45 % |
| Cobble = 40 % |
| Gravel = 10 % |
| Sand = 5 % |
| Parameter | Sample Date | Sample value | All data median | All data 10th percentile | All data 90th percentile | Reference 10th percentile | Reference 90th percentile | Units |
|---|---|---|---|---|---|---|---|---|
| Dissolved Oxygen | 2017-07-10 | 9.51 | 8.60 | 7.00 | 10.23 | 7.80 | 10.62 | Milligrams Per Liter |
| pH | 2017-07-10 | 7.74 | 7.12 | 6.21 | 7.97 | 6.00 | 7.55 | Standard Ph Unit |
| Specific Conductance | 2017-07-10 | 589 | 88.55 | 25.00 | 492.00 | 15.41 | 67.31 | Microsiemens Per Centimeter |
| Temperature | 2017-07-10 | 23 | 20.00 | 14.70 | 24.70 | 12.80 | 23.60 | Degrees Celcius (Temperature) |
| Nitrate + Nitrite As Nitrogen | 2017-07-10 | 0.03 | 0.08 | 0.02 | 0.61 | 0.01 | 0.09 | Milligrams Per Liter |
| Orthophosphate As Phosphorus | 2017-07-10 | 2 | 2.00 | 1.00 | 11.00 | 1.00 | 3.00 | Micrograms Per Liter |
| Total Alkalinity | 2017-07-10 | 5.8 | 19.50 | 4.44 | 113.20 | 2.00 | 21.00 | Milligrams Per Liter |
| Total Kjeldahl Nitrogen | 2017-07-10 | 0.4 | 0.40 | 0.20 | 0.60 | 0.10 | 0.50 | Milligrams Per Liter |
| Total Phosphorus | 2017-07-10 | 22 | 18.00 | 7.00 | 48.00 | 4.00 | 18.00 | Micrograms Per Liter |
| Cover type | Percent cover | Cover group |
|---|---|---|
| Sand / Mud | 2.86 | Not algae |
| Mat Incomplete | 53.33 | Thin algal layer |
| Mat <1mm Thick | 43.81 | Thin algal layer |
| Land Cover Data Source: | MELCD 2004 |
| Watershed Area (sq km): | |
| Impervious Cover %: |
| Cover Type | Percent | Category |
|---|---|---|
| No data | No Data | No data |
| Name: | Stone Brook - Station 944 | Sampled by: | Biomonitoring Unit |
| Town: | Augusta | Method: | Rock Scrapings 1 Inch Circles |
| Biomonitoring Basin | Kennebec | Sample ID: | SA-944-2017R (1677) |
| Sample Date: | 2017-07-10 | Taxonomist: | Ecoanalysts Idaho |
Tolerance values color coding: Blue for sensitive, <32.20.
Purple for intermediate, >=32.20 and <60. Red for tolerant,
>=60.
| Name | Group | RA | RB | Oxy | Sap | Sal | Tr | Mot | GF | Tol | TN | TP |
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Achnanthidium minutissimum | Pennate Diatom | 0.311 | 0.025 | 1 | 2 | 2 | 7 | N | P | 41.2 | ||
| Encyonema silesiacum | Pennate Diatom | 0.116 | 0.087 | 3 | 3 | 2 | 7 | V | S | 46.9 | 43 | 69 |
| Achnanthidium deflexum | Pennate Diatom | 0.072 | 0.013 | 1 | 2 | 3 | N | P | 43.5 | 40 | 52 | |
| Heteroleibleinia | Filamentous Cyanobacteria | 0.070 | 0.000 | NA | 22 | 22 | ||||||
| Fragilaria capucina | Pennate Diatom | 0.038 | 0.005 | 2 | 2 | 3 | N | V | 32.9 | 59 | 51 | |
| Encyonema leibleinii | Pennate Diatom | 0.033 | 0.402 | V | S | NA | ||||||
| Caloneis bacillum | Pennate Diatom | 0.029 | 0.018 | 2 | 2 | 2 | 4 | M | P | 64.9 | 72 | 96 |
| Unknown Rhodophyte Florideophycidae (Chantransia) | Red Algae | 0.027 | 0.013 | 47.5 | 48 | 68 | ||||||
| Diatoma moniliformis | Pennate Diatom | 0.027 | 0.007 | 3 | N | U | 52.8 | 27 | 36 | |||
| Amphora pediculus | Pennate Diatom | 0.023 | 0.003 | 2 | 2 | 2 | 5 | M | P | 76.2 | 71 | 93 |
| Nitzschia dissipata | Pennate Diatom | 0.023 | 0.009 | 2 | 2 | 2 | 4 | H | P | 60.9 | 48 | 75 |
| Cocconeis placentula | Pennate Diatom | 0.017 | 0.019 | 3 | 2 | 2 | 5 | N | P | NA | 30 | 82 |
| Gomphonema | Pennate Diatom | 0.017 | 0.017 | N | S | 15.1 | ||||||
| Synedra rumpens | Pennate Diatom | 0.015 | 0.003 | 2 | 2 | N | E | 34.3 | 20 | 32 | ||
| Navicula cryptocephala | Pennate Diatom | 0.015 | 0.008 | 3 | 3 | 2 | 7 | M | P | 56.3 | 55 | 80 |
| Navicula gregaria | Pennate Diatom | 0.015 | 0.005 | 4 | 3 | 3 | 5 | M | P | 79.6 | 66 | 89 |
| Cyclotella meneghiniana | Centric Diatom | 0.012 | 0.013 | 5 | 4 | 3 | 5 | N | U | 72.6 | 55 | 73 |
| Fragilaria vaucheriae | Pennate Diatom | 0.012 | 0.004 | 3 | 3 | 2 | 5 | N | V | 44.2 | 36 | |
| Gomphonema calcifugum | Pennate Diatom | 0.008 | 0.003 | N | S | NA | ||||||
| Gomphonema micropus | Pennate Diatom | 0.008 | 0.005 | 2 | 2 | 2 | 5 | N | S | 39 | 72 | 89 |
| Meridion circulare | Pennate Diatom | 0.008 | 0.007 | 2 | 2 | 2 | 7 | N | E | 46.5 | 64 | 87 |
| Gogorevia exilis | Pennate Diatom | 0.006 | 0.001 | 1 | 2 | 2 | 7 | N | P | 51.1 | 63 | 91 |
| Ctenophora pulchella | Pennate Diatom | 0.006 | 0.017 | 3 | 5 | 2 | 3 | N | E | 49.7 | ||
| Rhoicosphenia abbreviata | Pennate Diatom | 0.005 | 0.007 | 2 | 2 | 2 | 5 | V | S | 83.4 | 72 | 96 |
| Ulnaria ulna | Pennate Diatom | 0.005 | 0.145 | 3 | 4 | 2 | N | E | 34.2 | 17 | 21 | |
| Navicula rhynchocephala | Pennate Diatom | 0.005 | 0.005 | 4 | 2 | 2 | 7 | M | P | 62.1 | 44 | 78 |
| Eolimna minima | Pennate Diatom | 0.005 | 0.001 | 4 | 4 | 2 | 5 | M | P | 57 | 64 | 88 |
| Eunotia | Pennate Diatom | 0.005 | 0.007 | V | E | NA | ||||||
| Gomphonema parvulum | Pennate Diatom | 0.005 | 0.001 | 4 | 4 | 2 | 5 | N | S | 42.2 | 21 | |
| Gomphonema truncatum | Pennate Diatom | 0.005 | 0.025 | 2 | 2 | 2 | 4 | N | S | 36.5 | 47 | 44 |
| Karayevia clevei | Pennate Diatom | 0.005 | 0.001 | 2 | 2 | 2 | 4 | V | P | 54.3 | 72 | |
| Melosira varians | Centric Diatom | 0.005 | 0.035 | 3 | 3 | 2 | 5 | N | U | 67 | 67 | 89 |
| Navicula canalis | Pennate Diatom | 0.005 | 0.002 | 2 | 5 | M | P | NA | 50 | 89 | ||
| Nitzschia | Pennate Diatom | 0.005 | 0.004 | H | P | NA | ||||||
| Navicula lundii | Pennate Diatom | 0.003 | 0.003 | 2 | 2 | 2 | 5 | M | P | NA | ||
| Diatoma vulgaris | Pennate Diatom | 0.003 | 0.017 | 2 | 2 | 2 | 4 | N | U | 88.7 | 60 | 89 |
| Fragilaria crotonensis | Pennate Diatom | 0.003 | 0.002 | 2 | 2 | 2 | 3 | N | V | NA | 53 | 64 |
| Navicula seibigiana | Pennate Diatom | 0.003 | 0.001 | M | P | NA | ||||||
| Nitzschia archibaldii | Pennate Diatom | 0.003 | 0.000 | 2 | 2 | 2 | 5 | H | P | 60 | ||
| Nitzschia linearis | Pennate Diatom | 0.003 | 0.013 | 2 | 2 | 2 | 4 | H | P | 54.2 | 68 | 87 |
| Nitzschia palea var. debilis | Pennate Diatom | 0.003 | 0.001 | 1 | 1 | 1 | H | P | 53.4 | 47 | 79 | |
| Nitzschia recta | Pennate Diatom | 0.003 | 0.007 | 2 | 2 | 2 | 7 | H | P | 46.6 | 43 | 73 |
| Platessa bahlsii | Pennate Diatom | 0.003 | 0.000 | V | P | NA | ||||||
| Sellaphora seminulum | Pennate Diatom | 0.002 | 0.000 | 4 | 4 | 2 | 5 | M | P | 51.5 | 67 | 73 |
| Simonsenia delognei | Pennate Diatom | 0.002 | 0.000 | 1 | 3 | 3 | 5 | M | P | NA | ||
| Surirella minuta | Pennate Diatom | 0.002 | 0.002 | 3 | 3 | 2 | 5 | H | P | 79.7 | 69 | 95 |
| Planothidium frequentissimum | Pennate Diatom | 0.002 | 0.001 | 3 | 4 | 2 | V | P | 65.1 | 69 | 92 | |
| Cymbopleura naviculiformis | Pennate Diatom | 0.002 | 0.001 | 2 | 2 | 2 | 5 | V | S | 51.6 | 35 | 53 |
| Diploneis elliptica | Pennate Diatom | 0.002 | 0.022 | 1 | 1 | 2 | 3 | M | P | NA | ||
| Gomphonema minusculum | Pennate Diatom | 0.002 | 0.002 | N | S | NA | 38 | 51 | ||||
| Gomphonema pumilum | Pennate Diatom | 0.002 | 0.000 | 2 | 7 | N | S | 43.6 | 14 | 21 | ||
| Hippodonta hungarica | Pennate Diatom | 0.002 | 0.000 | 3 | 2 | 2 | 4 | M | P | NA | ||
| Navicula perminuta | Pennate Diatom | 0.002 | 0.000 | M | P | NA | ||||||
| Pinnularia gibba | Pennate Diatom | 0.002 | 0.007 | 3 | 3 | 2 | 7 | M | P | NA | ||
| Navicula tripunctata | Pennate Diatom | 0.002 | 0.002 | 2 | 2 | 2 | 5 | M | P | 69.4 | 76 | 88 |
| Column | Name | Description |
|---|---|---|
| RA | Relative Abundance | number of cells (density of cells per square centimeter) in a sample / total abundance of all taxa |
| RB | Relative Biovolume | Volume of a taxon’s cells in a sample / volume of all algae cells in a sample |
| Oxy | van Dam Oxygen tolerance | 1=100% DO saturation, 2=>75% DO saturation, 3=>50% DO saturation, 4=>30% DO saturation, 5=<30% DO saturation |
| Sap | van Dam Saprobic value | Saprobic values relate to the amount of organic pollution, biological oxygen demand, and DO concentrations. Values range from 1 (intolerant of organic pollution) to 5 (highly tolerant of organic pollution) |
| Sal | van Dam Salinity value | 1=freshwater (<100 mg/L chloride) , 2=fresh-brackish (<500 mg/L), 3=brackish-freshwater (500-1000 mg/L), 4=brackish (1000-5000 mg/L) |
| Tr | van Dam Trophic value | 1=oligotraphentic, 2=oligo-mesotraphentic, 3=mesotraphentic, 4=meso-eutraphentic, 5=eutraphentic, 6=hypereutraphentic, 7=indifferent to trophic state |
| Mot | Motility of Diatoms | Motility (capability of movement in water or on substrates) based on genus (Wang et al. 2005): N= not motile, M = motile , H = highly motile, V=variable within genus |
| GF | Growth Forms | E= erect, P=prostrate, S=stalked, U=unattached, V=variable (based on communication with R. Jan Stevenson) |
| Tol | Tolerance value | Tolerance to a combination of watershed disturbance, conductivity, and nutrient enrichment (based on Maine data). Value range from 1=most senstive to 100=most tolerant. |
| TN | TN value | Preference for total nitrogen (TN) based on Maine data. Values range from 1=low TN concentrations to 100=high TN concentrations. |
| TP | TP value | Preference for total phosphorus (TP) based on Maine data. Values range from 1=low TP concentrations to 100=high TP concentrations. |