Lecture 8 - Point Source Pollution

Point Sources of Pollutants

  • Definition:
    • A substance becomes a pollutant when the receiving water's capacity to degrade, disperse, or dilute it is exceeded.
    • Exceeded means dilution, dispersion, or degradation cannot prevent harm to the aquatic ecosystem or legitimate (human) uses.
    • This definition implies that discharge is permissible as long as the processes of dilution, degradation, and dispersion protect the ecosystem and human uses. The primary focus is on dilution potential.
  • Key Aspects:
    • Identifiable Source: Must be able to identify the source of entry into the receiving water.
    • Permitting: The ability to permit the entry, enabling treatment.
    • Treatment: Permits drive treatment and investment in treatment.
    • Monitoring: The site is monitored for compliance.

Diffuse vs. Micro Point Sources

  • Diffuse Sources: Classically, diffuse sources are not manageable in the same way due to the lack of an identifiable entry point.
  • Micro Point Sources: Small point sources, like septic tank systems, often lack identifiable discharge points, hindering permitting, treatment, and monitoring.

Wastewater Sources

  • Domestic Wastewater Treatment Works: Traditional focus, exemplified by the Lancaster wastewater treatment works.
  • Industrial Sources: Increasingly important to consider.
    • Examples: Discharges from industrial complexes, textile industries (detergents causing foam), and mixed industrial/domestic waste in rivers like the Ganges.

Industrial Effluent Categories

  • Heavy Industries: Wastewater from heavy industrial processes.
  • Light Industrial Work: E.g., the textile industry.
  • Food Industry: E.g., breweries, milk/cheese processing plants generating wastewaters high in glutens.

Management of Industrial Discharges

  • On-site Treatment: Industrial sites treat their wastewater and comply with permits.
  • Trade Effluent to Sewer: Industrial wastewater sent to municipal wastewater treatment plants (e.g., Lancaster), with the utility charging the industrial sites for treatment.

Permitting Framework

  • Objective: To control discharges from point sources to prevent harm to the aquatic ecosystem and human uses.
  • Legislative Basis:
    • Legislation (e.g., Urban Wastewater Treatment Directive) sets minimum baselines.
    • The Environment Agency can set permits for substances not in legislation or impose stricter limits.

Approaches to Permitting

  • Uniform Approach:
    • Based on size (person equivalent) or type of discharge.
    • Problem: Does not account for the receiving water's capacity to handle the wastewater.
  • Catchment Based Approach:
    • Sets a permit for the entire catchment (e.g., total phosphorus discharge).
    • Problem: Does not account for the specific location of individual point sources.
  • Site Based Permitting:
    • Informed by local conditions and the capacity of the receiving water.
    • Administrative burden but protects local differences.

Critical Load

  • Definition: The threshold at which a receiving water can no longer handle the pollutant load from a point source without causing damage.

Critical Load Management: Mass Balance

  • Conceptualization:
    • Considers a river reach with a point source discharge.
    • Accounts for loads from upstream tributaries, diffuse sources, subsurface (groundwater) discharges, and losses/gains within the reach.
    • The load is concentration times discharge (Load=ConcentrationDischargeLoad = Concentration Discharge).

Dilution Modeling

  • Simplification of Mass Balance:
    • Focuses on upstream load, effluent load, losses/gains, and downstream load.
    • Equation: Q<em>uC</em>u+Q<em>eC</em>e+L=Q<em>dC</em>dQ<em>uC</em>u + Q<em>eC</em>e + L = Q<em>dC</em>d
      • Where:
        • QQ = discharge
        • CC = concentration
        • uu = upstream
        • ee = effluent
        • dd = downstream
        • LL = losses or gains
    • Units must be consistent.

Mass Balance Principle

  • Rate of change of mass is determined by what comes in minus what leaves.
  • Equation: Δ(Q<em>dC</em>d)Δt=Q<em>uC</em>u+Q<em>eC</em>eQ<em>dC</em>d\frac{\Delta (Q<em>dC</em>d)}{\Delta t} = Q<em>uC</em>u + Q<em>eC</em>e - Q<em>dC</em>d

Simplifications for Permitting

  • No Loss or Accumulation: The substance is conservative (L = 0).
  • Perfect Mixing: Effluent mixes perfectly with the upstream tributary at the point of contact.
  • No Change of Mixed Mass Through Time: The rate of change of mass is zero.

Conservative Dilution

  • Equation: Q<em>uC</em>u+Q<em>eC</em>eQ<em>dC</em>d=0Q<em>uC</em>u + Q<em>eC</em>e - Q<em>dC</em>d = 0
  • What goes into the reach is what leaves.

Rearranging the Equation

  • To estimate downstream concentration (CdC_d):
    • C<em>d=Q</em>uC<em>u+Q</em>eC<em>eQ</em>dC<em>d = \frac{Q</em>uC<em>u + Q</em>eC<em>e}{Q</em>d}
    • Where Q<em>d=Q</em>u+QeQ<em>d = Q</em>u + Q_e

Data Requirements

  • Effluent Concentration: From consent or estimate.
  • Effluent Discharge: Estimated from dry weather flow.
  • Upstream Discharge: Monitoring data.
  • Upstream Concentration: Monitoring data or Water Framework Directive class boundaries.

Limitations of Conservative Dilution

  • Instantaneous Values: Only works for specific values of Q<em>eQ<em>e, C</em>eC</em>e, Q<em>uQ<em>u, and C</em>uC</em>u.
  • Statistical Descriptors: Permits are based on statistical descriptors of a distribution (e.g., 90th percentile).
  • Not Robust for Percentiles: Standard conservative dilution is not robust when using 90th percentiles.

Combined Distribution Approach

  • Uses a distribution of values for inputs (QU, CU, QE, CE) to generate a distribution of values for the downstream concentration.
  • Enables calculation of percentile BOD or DO concentrations to assess compliance with WFD classes.
  • Can be implemented using Monte Carlo simulation.

Permit Components

  • 90th Percentile or Mean: For total P and total N.
  • MAC (Maximum Allowable Concentration): An upper-tier limit, often set as double the 90th percentile.
  • Two Modeling Frameworks: Simple conservative dilution and combined distribution.

Wastewater Composition

  • Predominantly Water: 99.9% by mass.
  • Solids: 0.1%, mostly organic compounds (fats, carbohydrates, proteins).
  • Inorganic Fraction: Grits, metal, salt, glass, etc.

Pollutant Concentrations in Raw Wastewater

  • BOD: ~300 mg/L (limit under Urban Waste Water Treatment Directive is 25 mg/L).
  • COD: ~400 mg/L (limit under Urban Waste Water Treatment Directive is 125 mg/L).
  • Total N: ~40 mg/L
  • Phosphorus: ~10 mg/L
  • Stoichiometry: High N and P relative to C.

Emerging Contaminants

  • Endocrine Disruptors:
    • Interfere with the endocrine system (hormone secretion).
    • Examples: Estrogen, pesticides, dioxins, PCBs.
    • Limited evidence on environmental quality standards and effects.
    • Example: Male fish developing deformities when exposed to synthetic estrogen.
  • Pharmaceuticals and Personal Care Products (PPCPs):
    • Examples: Caffeine, ibuprofen, diazepam, prescription drugs.
    • Potential effects on ecosystems.
  • Illicit Drugs: Monitoring in wastewater networks.
  • Microplastics: Another emerging concern.