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=ConcentrationDischarge).
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>d
- Where:
- Q = discharge
- C = concentration
- u = upstream
- e = effluent
- d = downstream
- L = 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: ΔtΔ(Q<em>dC</em>d)=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>e−Q<em>dC</em>d=0
- What goes into the reach is what leaves.
Rearranging the Equation
- To estimate downstream concentration (Cd):
- C<em>d=Q</em>dQ</em>uC<em>u+Q</em>eC<em>e
- Where Q<em>d=Q</em>u+Qe
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>e, C</em>e, Q<em>u, and C</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.