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Surface water routine parameter determination is essential for evaluating the environmental quality of rivers, lakes, and reservoirs and for verifying compliance with national and international water quality standards. This technical article outlines the core physical, chemical, and microbiological indicators used in routine surface water analysis, the standardized test methods published by ISO, ASTM, and GB/HJ standards bodies, and the practical applications of monitoring data in environmental management and regulatory reporting. Sampling requirements, quality control procedures, and frequently asked questions are also addressed to support laboratories, environmental agencies, and industrial stakeholders.

Technical Overview

Surface water refers to water occurring in rivers, streams, lakes, reservoirs, and other freshwater bodies open to the atmosphere, and it serves as a primary resource for drinking water production, irrigation, industry, and the maintenance of aquatic ecosystems. Routine parameter determination is the systematic measurement of a defined set of physical, chemical, and microbiological indicators that collectively characterize the general quality of a surface water body. These routine indicators form the backbone of most national monitoring programs and are used to classify water bodies, identify pollution trends, and evaluate the effectiveness of pollution control measures.

In China, the guiding framework is GB 3838-2002, Environmental Quality Standards for Surface Water, which assigns surface water to five quality grades (Grade I through Grade V) according to designated functions such as source water protection, aquatic habitat conservation, and industrial or agricultural use. Comparable international programs rely on ISO and ASTM analytical standards together with regional classification schemes. Routine determinations are typically performed by accredited third-party laboratories operating under ISO/IEC 17025 quality management systems, which ensures that reported data are traceable, defensible, and suitable for regulatory decision-making.

Testing Samples

Rivers and Streams

Grab or time-composite samples are collected at established monitoring cross-sections, typically at mid-channel and mid-depth. Additional sections are positioned upstream and downstream of wastewater outfalls, confluences, and industrial discharges to isolate pollution sources. Flow measurements are often recorded concurrently so that mass loads can be calculated alongside concentration data.

Lakes and Reservoirs

Stratified sampling is applied at central monitoring points to capture vertical quality differences between the epilimnion and hypolimnion, particularly during summer stratification. Nutrient and chlorophyll-related parameters are prioritized to support trophic state assessment and eutrophication control in these slower-exchanging water bodies.

Estuaries and Transitional Waters

Sampling in tidal reaches is coordinated with the tidal cycle to account for salinity gradients and seawater intrusion. Routine indicators such as salinity, turbidity, nutrients, and oxygen-demanding substances are interpreted against the mixing regime to distinguish anthropogenic impacts from natural variability.

Source Water Intakes and Background Sections

Raw water at drinking water intakes is monitored routinely to confirm suitability for treatment and to detect upstream contamination events. Background sections, located in relatively undisturbed headwaters, provide reference values against which downstream changes are compared.

Testing Items

Routine surface water testing programs generally cover the following indicator groups, with the exact parameter list selected according to the applicable standard, water function zone, and known local pressures.

Physical and General Indicators

  • Water temperature, color, odor, and transparency
  • pH value
  • Turbidity and suspended solids
  • Electrical conductivity and total dissolved solids
  • Oil film or floating matter, where visually observed

Oxygen-Balance Indicators

  • Dissolved oxygen (DO)
  • Five-day biochemical oxygen demand (BOD5)
  • Chemical oxygen demand by dichromate (CODCr)
  • Permanganate index (CODMn)

Nutrient and Eutrophication Indicators

  • Ammonia nitrogen (NH3-N)
  • Nitrate nitrogen and nitrite nitrogen
  • Total nitrogen (TN)
  • Total phosphorus (TP)

Inorganic Non-Metallic Indicators

  • Fluoride, chloride, and sulfate
  • Cyanide and sulfide
  • Total hardness and alkalinity, where relevant

Metal Indicators

  • Copper, zinc, lead, cadmium, iron, and manganese
  • Hexavalent chromium and total chromium
  • Arsenic, selenium, and mercury

Organic and Microbiological Indicators

  • Volatile phenols
  • Petroleum hydrocarbons
  • Anionic surfactants
  • Fecal coliform bacteria and total coliform bacteria

Testing Methods

Sampling, Preservation, and Holding Times

Sampling is conducted in accordance with the ISO 5667 series and Chinese technical specifications such as HJ 91.1 and HJ 493. Samples are collected into pre-cleaned glass or polyethylene containers appropriate to each analyte, and representative aliquots are taken at the specified depth and position. Preservation measures are applied immediately to stabilize analyte concentrations, and samples are transported under refrigeration to the laboratory within defined holding times.

  • Metals: filtered or unfiltered aliquots acidified with nitric acid to pH below 2
  • COD and ammonia nitrogen: acidified with sulfuric acid to pH below 2 and stored at approximately 4 degrees Celsius
  • Total nitrogen and total phosphorus: acidified and refrigerated
  • BOD5 and dissolved oxygen: analyzed promptly with zero headspace where DO is measured by the iodometric method
  • Volatile phenols, cyanide, and sulfide: alkalized as required and protected from light
  • Microbiological parameters: sterile containers, transport at low temperature, and analysis ideally within 6 to 8 hours

Standard Analytical Techniques

Each routine parameter is measured using a recognized reference method, with instrumental techniques increasingly preferred for sensitivity, throughput, and multi-element capability. Commonly applied methods include the following.

  • pH: glass electrode method (GB 6920, ISO 10523)
  • Dissolved oxygen: iodometric method (GB 7489, ISO 5813) or electrochemical probe method (HJ 506, ISO 5814, ASTM D888)
  • CODCr: dichromate digestion with titrimetric or spectrophotometric finish (HJ 828, GB 11914, ISO 6060, ASTM D1252)
  • Permanganate index: acidic potassium permanganate oxidation (GB 11892)
  • BOD5: dilution and inoculation method (HJ 505, ISO 5815-1)
  • Ammonia nitrogen: Nessler spectrophotometry (HJ 535) or salicylate spectrophotometry (HJ 536)
  • Total nitrogen: alkaline potassium persulfate digestion with ultraviolet spectrophotometry (HJ 636, GB 11894, ISO 11905-1)
  • Total phosphorus: ammonium molybdate spectrophotometry (GB 11893, ISO 6878)
  • Turbidity: nephelometric method (HJ 1075, ISO 7027, ASTM D1889)
  • Suspended solids: gravimetric filtration method (GB 11901)
  • Fluoride, chloride, and sulfate: ion chromatography (HJ 84) or ion-selective electrode for fluoride (GB 7484)
  • Cyanide: distillation followed by spectrophotometric or flow-analysis detection (HJ 484)
  • Volatile phenols: 4-aminoantipyrine spectrophotometry (HJ 503, ISO 6439)
  • Petroleum: infrared spectrophotometry (HJ 637, HJ 970)
  • Anionic surfactants: methylene blue active substances spectrophotometry (GB 7494, ISO 7875-1)
  • Metals: inductively coupled plasma mass spectrometry (HJ 700, ISO 17294-2), inductively coupled plasma optical emission spectrometry (HJ 776), or atomic absorption spectrometry (GB 7475), with cold vapor and hydride generation techniques for mercury, arsenic, and selenium (HJ 597, HJ 694)
  • Hexavalent chromium: 1,5-diphenylcarbazide spectrophotometry (GB 7467)
  • Fecal coliform: membrane filtration, multiple-tube fermentation, or enzyme substrate methods (HJ 347.1, HJ 347.2)

Quality Assurance and Quality Control

Accredited third-party laboratories validate routine determinations through method blanks, laboratory control samples, matrix spikes, duplicate analyses, calibration verification, and certified reference materials. Control charts, measurement uncertainty estimation, and inter-laboratory comparisons further demonstrate the reliability of reported results in accordance with ISO/IEC 17025 requirements.

Applications

Data generated from routine surface water parameter determination support a wide range of environmental management objectives across governmental, municipal, and industrial contexts.

  • Regulatory compliance monitoring and periodic environmental quality reporting for rivers, lakes, and reservoirs
  • Environmental impact assessments for construction projects and industrial facilities
  • Verification of wastewater discharge compliance and evaluation of receiving-water response under discharge standards such as GB 8978
  • Drinking water source protection and early warning of contamination events at raw water intakes
  • Eutrophication control, harmful algal bloom early warning, and nutrient load reduction programs
  • Pollution incident investigation, source tracing, and ecological restoration effectiveness evaluation
  • Scientific research, water quality modeling, and long-term trend analysis in watershed management

FAQ

What are routine parameters in surface water analysis?

Routine parameters are the core physical, chemical, and microbiological indicators measured on a recurring basis to characterize general water quality, including pH, dissolved oxygen, COD, permanganate index, BOD5, ammonia nitrogen, total nitrogen, total phosphorus, suspended solids, selected metals, petroleum, volatile phenols, anionic surfactants, and fecal coliform bacteria.

Which standards define surface water quality requirements?

In China, GB 3838-2002 establishes the environmental quality standards and the five-grade classification system for surface water, while HJ-series standards specify the corresponding analytical and sampling methods. Internationally, ISO and ASTM standards provide equivalent test procedures that are widely accepted for cross-border projects and research.

What is the difference between COD and the permanganate index?

COD measured by the dichromate method quantifies nearly all oxidizable organic and inorganic matter and is mainly applied to wastewater and heavily polluted water. The permanganate index uses potassium permanganate under milder conditions, oxidizes only the more reactive fraction of organics, and is the preferred oxygen-consumption indicator for relatively clean surface water.

How should surface water samples be preserved and transported?

Samples should be collected into analyte-appropriate containers, chemically preserved where required, chilled to approximately 4 degrees Celsius, shielded from light, and delivered to the laboratory within the holding time specified for each parameter. Metals aliquots are typically acidified to pH below 2, while microbiological samples must remain sterile and be analyzed as soon as practicable.

How frequently is routine surface water monitoring performed?

Monitoring frequency depends on the water function zone and program objectives. National and provincial monitoring sections are commonly sampled monthly or quarterly, drinking water sources may be monitored weekly or continuously for key parameters, and special investigations during pollution episodes or algal bloom seasons may require daily or even higher-frequency sampling.

Why are ammonia nitrogen and total nitrogen both monitored?

Ammonia nitrogen reflects the most recent inputs of decomposable organic pollution and is directly toxic to aquatic life at elevated concentrations, whereas total nitrogen captures the complete pool of organic and inorganic nitrogen species driving eutrophication. Comparing the two helps distinguish fresh pollution discharges from accumulated nutrient loads and guides targeted remediation strategies.