USDA LTAR Common Experiment measurement: Total suspended solids (TSS)

Brent Dalzell, Oliva Pisani

Published: 2024-08-15 DOI: 10.17504/protocols.io.261ge5pjog47/v2

Disclaimer

This research is a contribution from the Long-Term Agroecosystem Research (LTAR) network. LTAR is supported by the United States Department of Agriculture. The use of trade, firm, or corporation names in this publication is for the information and convenience of the reader. Such use does not constitute an official endorsement or approval by the United States Department of Agriculture or the Agricultural Research Service of any product or service to the exclusion of others that may be suitable. USDA is an equal opportunity provider and employer.

Abstract

Total suspended solids (TSS) refers to all the material from a well-mixed sample retained by a filter media. In the case of environmental water samples, TSS is commonly used to measure sediment in surface waters (field runoff, ditches, and streams) but can also be present in subsurface flow where macropore flow or surface inlets to tile drainage systems are present. In some cases, TSS can also include algae or other plant materials that comprise volatile suspended solids (VSS) because combustion in a muffle furnace eliminates them. The recommended method for measuring TSS includes passing a known sample volume through a pre-weighed filter and measuring the oven-dry weight of the material trapped on the filter.

Steps

Sample collection

1.

At a minimum, collect 1mg of TSS residue. At a maximum, TSS should not impede the flow rate of the filter media (slow filtration is more time-consuming but does not impact results).

Note
The required sample volume will vary with site and event characteristics. For many environmental samples, 100mL of sample solution is a reasonable starting point if using a 4.7 cm diameter filter disc.

2.

Return samples to the laboratory On ice and filter them on collection day if possible.

Sample storage and preservation

3.

Analyze the samples as soon as possible after collection.

4.

If storage is required, refrigerate the samples at 4°C or store On ice to minimize decomposition of solids.

Note
Samples should not be stored for more than seven days (APHA, 2005). Samples should be at Room temperature for analysis.

Archiving

5.

Store water samples for TSS analyses until data certification (QA/QC verification) as this is common practice.

Note
Water sample storage should not exceed seven days.

Glass fiber filter preparation

6.

Assemble the vacuum filtration apparatus with a new filter.

7.

Apply the vacuum.

8.

Rinse the filter three times with distilled water.

9.

Maintain the vacuum for a few seconds to remove excess water, then remove the vacuum.

10.

Using forceps, carefully remove the rinsed filter to an aluminum weighing dish.

11.

Dry in an oven at 103°C - 105°C for 1 hour.

12.

Store dried filters in a desiccator until needed.

Sample analysis

13.

Using forceps, select a prepared glass fiber filter. Weigh it and record the mass to the nearest 0.1 mg in a lab notebook.

14.

Unless filtering the entire sample, shake it vigorously before dividing it into a volume suitable for analysis.

15.

Select a water sample, weigh the sample + bottle mass, and record the mass in a lab notebook.

16.

Assemble the filtration apparatus and apply a vacuum.

17.

Pre-moisten the filter with a small volume of distilled water.

18.

Shake the sample vigorously and pour it into the filtration apparatus funnel.

19.

Maintain the vacuum until all sample water has passed through the filter.

20.

Using a wash bottle with distilled water, rinse the sample bottle and sides of the filter funnel three times (for a 4.7 cm filter, each rinse should be roughly 10 ml).

21.

Weigh the empty sample bottle and record the mass in a lab notebook.

22.

Remove the vacuum.

23.

Using forceps, carefully remove the filter paper and place it in a labeled and weighed aluminum weighing dish.

24.

Dry the filter paper + sample at 105°C for 1 hour or longer, if necessary, to remove all water.

25.

Remove the samples from the oven and immediately store them in a desiccator or weigh them. Record the mass in a lab notebook.

26.

Store the weighed and recorded filters in a desiccator until ready for disposal.

27.

Sample the covariate metrics (Total N (TN) and total P (TP) concentrations) concurrently.

28.

Perform the calculations using the following formula:

Total suspended solids in a sample (mg/L) = (A-B) * 1000 / C

Note
A = mass of filter and weighing dish + sample residue (mg)B = mass of filter and weighing dish (mg)C = volume of sample (ml); (mass of bottle with sample - mass of empty bottle) C can also be obtained directly by pouring the sample into a graduated cylinder and recording the sample volume. The *1000 term in the equation above is a conversion factor to result in final units of mg/L.

Recommendations for data collection

29.

Table 1. Summary of recommendations for the collection and measurement of TSS concentration.

ABCD
AttributePreferredMinimumComments
Spatial scaleFieldPlot
FrequencyEvent-drivenEvent-drivenSample collection frequency will depend on site-specific flow chracteristics and experimental goals
Covariate metricsTN, TPTN, TP
Sample preservation and storageAnalyze on collection dayRefrigerate at 4°C or store on ice for up to 7 days
Sample analysisTotal suspended solids dried at 103-105°C
Water quantityDischarge or flow rateDischarge or flow rateCalculate TSS loads by linking this metric to the water quantity metric “flow"

Covariate metrics = other metrics to sample concurrently. TN = total nitrogen; TP = total phosphorus.

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