20 June 2013 Prague, Czech Republic

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20 June 2013 Prague, Czech Republic. Advances in US Lead Producer Emission Controls. Russell Kemp Atlanta, Georgia USA rkemp@environcorp.com. Overview and Update. New rules in US spurring substantial spending on additional emission controls - PowerPoint PPT Presentation

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20 June 2013Prague, Czech Republic

Russell KempAtlanta, Georgia USArkemp@environcorp.com

Advances in US Lead ProducerEmission Controls

2

Overview and Update

• New rules in US spurring substantial spending on additional emission controls

• 2008 revision to National Ambient Air Quality Standard for Lead– Ten-fold reduction to 0.15 ug/m3 three-month rolling avg.– Currently in implementation phase

• 2012 revision to National Emission Standard for Hazardous Air Pollutants for both primary and secondary lead smelting– Secondary Lead compliance Deadline January 2014

3

Fugitive Emission Controls

• Key element in achieving low ambient fenceline concentrations is reduction of fugitive emissions – driven by the lowered ambient standard

• New Emission Standard includes requirement to place all furnace operations, battery breakers, and feed storage rooms within negative pressure enclosures– To 0.007 inches water (0.013 mmHg, 1.7 Pa)– Continuously monitored

4

New, large full process enclosures being constructed (Battery Wrecker Enclosure)

5

A “before” view

6

An “after” view

7

Ambient monitoring network

8

Ambient Monitor Results

9

Stack Emission Progress

• New Secondary Lead Emission Standard– Cuts allowed stack exhaust concentration from 2 mg/dscm Pb to 1 mg/dscm for any one stack

• Facility-wide, airflow-weighted average limited to 0.2 mg/dscm

• Growing deployment of secondary (post-baghouse) HEPA filtration– For both goals, the new ambient standard and the new

emission standard• Lowest metals emission rates being achieved by

Wet Electrostatic Precipitators downstream of baghouses

10

Wet Electrostatic Precipitator (WESP)

• WESP installation completed at two US facilities, with third unit in final design phase followed by construction. WESP utilized to remove unfilterable sub-micron particles, including arsenic, and condensable gases.

• WESP downstream of conventional baghouses for all process emissions from dryer, furnaces & refinery kettles. Total Pb emissions from WESP < 2.3 kg/yr (<5 lb/yr).

• Balance of facility ventilation systems provide negative pressure for all total enclosures housing processes and equipped with HEPA secondary filtration.

• WESP and HEPAs support potential of < 11.3 kg/yr (25 lb/yr) facility-wide lead emissions from large capacity facilities.

11

WESP Installation 1, nominal 100,000 cfm (170,000 m3/hr)

12

WESP Installation 2, nominal 130,000 cfm (220,000 m3/hr)

13

WESP Performance (Installation 1)

Note: Installation 2 exhibits comparable results

614.95

8.58 0.81 1.22 3.59 1.800

100

200

300

400

500

600

700

pre-WESP Nov-08 Jun-09 Nov-09 Nov-10 Oct-12 (Est.)

Lead (Pb) Emissions

Lead (Pb) lbs/yr

14

WESP Performance (Installation 1)Note: Installation 2 exhibits comparable results

96.01

8.67 4.56 1.59 2.89 5.630

20

40

60

80

100

120

pre-WESP Nov-08 Jun-09 Nov-09 Nov-10 Oct12 (Est.)

Arsenic (As) Emissions

Arsenic (As) lbs/yr

15

US EPA Moving to Retain Ambient Lead Standard

• National Ambient Air Quality Standards (NAAQS) must be reviewed every five years

• EPA is in midst of review of the 2008 lowered standard

• On 05 May 2013, EPA’s full Clean Air Scientific Advisory Committee approved its Lead Review Panel’s conclusion that the available scientific evidence does not support revising the Pb NAAQS.

16

Dry scrubbingTo close with a cross-media development:

Facility required to eliminateSalt discharges to surface water

Eliminated up-front feed desulfurization, which generated sulfate water discharge

Installed dry lime scrubber downstream of primary metal emission control baghouse to control SO2

All while EPA’s new 1-hour SO2 NAAQS being implemented

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